Abstract

In this study we examined abiotic and biotic factors that could potentially influence the presence of a non-indigenous seaweed, Eucheuma denticulatum, in two locations, one outside (Kane’ohe Bay, Hawai’i, USA) and one within (Mafia Island, Tanzania) its natural geographical range. We hypothesized that the availability of hard substrate and the amount of wave exposure would explain distribution patterns, and that higher abundance of herbivorous fishes in Tanzania would exert stronger top–down control than in Hawai’i. To address these hypotheses, we surveyed E. denticulatum in sites subjected to different environmental conditions and used generalized linear mixed models (GLMM) to identify predictors of E. denticulatum presence. We also estimated grazing intensity on E. denticulatum by surveying the type and the amount of grazing scars. Finally, we used molecular tools to distinguish between indigenous and non-indigenous strains of E. denticulatum on Mafia Island. In Kane’ohe Bay, the likelihood of finding E. denticulatum increased with wave exposure, whereas on Mafia Island, the likelihood increased with cover of coral rubble, and decreased with distance from areas of introduction (AOI), but this decrease was less pronounced in the presence of coral rubble. Grazing intensity was higher in Kane’ohe Bay than on Mafia Island. However, we still suggest that efforts to reduce non-indigenous E. denticulatum should include protection of important herbivores in both sites because of the high levels of grazing close to AOI. Moreover, we recommend that areas with hard substrate and high structural complexity should be avoided when farming non-indigenous strains of E. denticulatum.

Highlights

  • Invasive species are considered to be a major threat to global marine biodiversity and ecosystem services (Schaffelke and Hewitt 2007; Katsanevakis et al 2014)

  • We investigated if non-indigenous strains of E. denticulatum have spread from areas of introduction (AOI) on Mafia Island

  • E. denticulatum and live coral cover were higher in Kane’ohe Bay whereas cover and number of other seaweed species, biomass of herbivorous fish and amount of soft substrate were higher on Mafia Island (Table 1)

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Summary

Introduction

Invasive species are considered to be a major threat to global marine biodiversity and ecosystem services (Schaffelke and Hewitt 2007; Katsanevakis et al 2014). Seaweeds (i.e., macroalgae) comprise a large part of non-indigenous species on a global scale (Bax et al 2003; Schaffelke and Hewitt 2007). Nonindigenous seaweeds can become invasive and influence ecosystem characteristics and functions by altering habitat complexity (Veiga et al 2014), community composition (Davidson et al 2015), biodiversity (Casas et al 2004; Schaffelke and Hewitt 2007) and ecosystem productivity (Sagerman et al 2014). Invasive seaweeds have been reported to induce and/or amplify coral-to-algal phase shifts in tropical reef systems (Schaffelke et al 2006; Williams and Smith 2007). To better understand potential risks and environmental consequences of introductions of nonindigenous seaweeds, there is a need to document occurrence and spread, and to identify environmental factors predicting their presence and abundance, especially if they become invasive

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