Abstract

Biological invasions represent grave threats to terrestrial, aquatic, and marine ecosystems, but our understanding of the role of evolution during invasions remains rudimentary. In marine environments, macroalgae account for a large percentage of invaders, but their complicated life cycles render it difficult to move methodologies and predictions wholesale from species with a single, free‐living ploidy stage, such as plants or animals. In haplodiplontic macroalgae, meiosis and fertilization are spatiotemporally separated by long‐lived, multicellular haploid and diploid stages, and gametes are produced by mitosis, not meiosis. As a consequence, there are unique eco‐evolutionary constraints that are not typically considered in invasions. First, selfing can occur in both monoicious (i.e., hermaphroditic) and dioicious (i.e., separate sexes) haplodiplontic macroalgae. In the former, fertilization between gametes produced by the same haploid thallus results in instantaneous, genome‐wide homozygosity. In the latter, cross‐fertilization between separate male and female haploids that share the same diploid parent is analogous to selfing in plants or animals. Separate sexes, therefore, cannot be used as a proxy for outcrossing. Second, selfing likely facilitates invasions (i.e., Baker's law) and the long‐lived haploid stage may enable purging of deleterious mutations, further contributing to invasion success. Third, asexual reproduction will result in the dominance of one ploidy and/or sex and the loss of the other(s). Whether or not sexual reproduction can be recovered depends on which stage is maintained. Finally, fourth, haplodiplontic life cycles are predicted to be maintained through niche differentiation in the haploid and diploid stages. Empirical tests are rare, but fundamental to our understanding of macroalgal invasion dynamics. By highlighting these four phenomena, we can build a framework with which to empirically and theoretically address important gaps in the literature on marine evolutionary ecology, of which biological invasions can serve as unnatural laboratories.

Highlights

  • Biological invasions represent one of the gravest threats to biodi‐ versity by altering ecosystem functioning and homogenizing native biota (Vitousek, Mooney, Lubchenco, & Melilo, 1997)

  • In the four subse‐ quent sections, I highlight unique eco‐evolutionary characteristics of haplodiplontic macroalgae: (a) Selfing can occur in both mono‐ icious and dioicious taxa with potential impacts on invasion dynamics; (b) while self‐ ing is linked to inbreeding depression, the long‐lived haploid stage may allow purging of the genetic load, reducing the costs associated with selfing; (c) due to the spatiotemporal separation of meiosis and fertilization, asexual reproduction will result in the loss, potentially irrevocably, of one the free‐living ploidies and/or sexes; and, (d) haploid and diploid stages may occupy different ecological niches, thereby strongly in‐ fluencing invasion dynamics and mating system variation

  • Otto and Marks (1996) Biological Journal of the Linnean Society, 57, 197–218. Few studies integrate both ecological and evolutionary pro‐ cesses in understanding responses to contemporary climate change (Anderson, Panetta, & Mitchell‐Olds, 2012; Rey et al, 2012), and spe‐ cifically biological invasions. This is in part because substantial amounts of information are necessary in order to distinguish between different eco‐evolutionary scenarios that facilitate invasions (Hufbauer et al, 2012), including (a) phenotypic data for native and non‐native popula‐ tions, (b) genetic data for documenting the invasion history, including mating system variation, and (c) biotic and abiotic environmental data to assess selection pressures acting across the extant range (Rey et al, 2012)

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Summary

Introduction

Biological invasions represent one of the gravest threats to biodi‐ versity by altering ecosystem functioning and homogenizing native biota (Vitousek, Mooney, Lubchenco, & Melilo, 1997).

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