Abstract

Facilitation cascades generated by co-occurring foundation species can enhance the abundance and diversity of associated organisms. However, it remains poorly understood how differences among native and invasive species in their ability to exploit these positive interactions contribute to emergent patterns of community structure and biotic acceptance. On intertidal shorelines in New England, we examined the patterns of coexistence between the native mud crabs and the invasive Asian shore crab in and out of a facilitation cascade habitat generated by mid intertidal cordgrass and ribbed mussels. These crab species co-occurred in low intertidal cobbles adjacent to the cordgrass–mussel beds, despite experimental findings that the dominant mud crabs can kill and displace Asian shore crabs and thereby limit their successful recruitment to their shared habitat. A difference between the native and invasive species in their utilization of the facilitation cascade likely contributes to this pattern. Only the Asian shore crabs inhabit the cordgrass–mussel beds, despite experimental evidence that both species can similarly benefit from stress amelioration in the beds. Moreover, only Asian shore crabs settle in the beds, which function as a nursery habitat free of lethal mud crabs, and where their recruitment rates are particularly high (nearly an order of magnitude higher than outside beds). Persistence of invasive adult Asian shore crabs among the dominant native mud crabs in the low cobble zone is likely enhanced by a spillover effect of the facilitation cascade in which recruitment-limited Asian shore crabs settle in the mid intertidal cordgrass–mussel beds and subsidize their vulnerable populations in the adjacent low cobble zone. This would explain why the abundances of Asian shore crabs in cobbles are doubled when adjacent to facilitation cascade habitats. The propensity for this exotic species to utilize habitats created by facilitation cascades, despite the lack of a shared evolutionary history, contributes to species coexistence and the acceptance of invasives into a diverse community.

Highlights

  • Understanding the factors that promote species coexistence, and enhance biodiversity, is a fundamental goal of ecology with important consequences for ecosystem functioning, community stability, and species conservation (Chesson, 2000; How to cite this article Altieri and Irving (2017), Species coexistence and the superior ability of an invasive species to exploit a facilitation cascade habitat

  • Surveys of habitat use and distributional overlap of crabs Our first survey of adult crab densities revealed that densities of Asian shore crabs in the low cobble zone were greater at sites with adjacent cordgrass-ribbed mussel beds in the mid zone than at sites without beds (F1,12 = 11.80, P < 0.001; Fig. 1), whereas mud crabs showed no difference between sites with and without adjacent beds (F1,12 = 4.14, P > 0.05)

  • Adult Asian crab density in low intertidal cobble revealed that densities of mud crab adults and recruits, as well as Asian shore crab adults, were highest in the low cobble zone with no difference between mid cobble and cordgrass–mussel beds, whereas Asian shore crab recruits were highest in the cordgrass–mussel beds with no difference between mid and low cobble zones (Fig. 2)

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Summary

Introduction

Understanding the factors that promote species coexistence, and enhance biodiversity, is a fundamental goal of ecology with important consequences for ecosystem functioning, community stability, and species conservation (Chesson, 2000; How to cite this article Altieri and Irving (2017), Species coexistence and the superior ability of an invasive species to exploit a facilitation cascade habitat. Species introductions provide an opportunity to examine the interactions that determine the ability of species to establish, persist, and coexist alongside other species (Sax, Stachowicz & Gaines, 2005). Recent theoretical developments predict that facilitation by native species can play an important role in the ability of an ecosystem to accommodate exotic species and thereby lead to positive relationships between native and invasive species (Bruno, Stachowicz & Bertness, 2003; Bulleri, Bruno & Benedetti-Cecchi, 2008). Foundation species, which create and modify habitats by ameliorating biotic and abiotic stresses, offer some of the best cases to test those predictions as to how facilitation can aid in the establishment of invasive species in both terrestrial and marine ecosystems (Altieri & Van De Koppel, 2013; Bulleri, 2009)

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