Abstract

Herbivores can drastically alter the morphology of macroalgae by directly consuming tissue and by inflicting structural wounds. Macroalgae host abundant and diverse epibiont communities, the dynamics of which tend to be mostly unknown in space and time. As the cultivation of macroalgae gains momentum worldwide, it is key to measure how epibionts could affect algal performance. We examined the epibiont community associated with farmed Alsidium triquetrum, a red macroalga with growing pharmacological interest. Measurements were conducted over two independent 60-day periods, one in summer and one in winter. Epibionts showed different patterns of succession in both seasons. Crustaceans, mainly amphipods, showed the highest overall density, with deleterious effects on daily growth rates of A. triquetrum in winter. Adverse effects as a function of epibionts were not detected in summer. A. triquetrum is a perennial alga. However, its performance as a crop in the nearshore can be significantly affected by the epibiont community structure that persists in winter. Amphipods and ascoglossan molluscs were risk factors in the mariculture of this agarophyte. In winter, they can destroy plants when they reach more than five individuals per gram of fresh biomass. Results highlight that commercial farming of A. triquetrum would be successful if grown throughout the summer.

Highlights

  • The increasing demand for macroalgal biomass has stimulated a global expansion of macroalgal farming [1]

  • It has encouraged research on species that are not yet domesticated but contain components of interest, for the biomedical and pharmacological industry [2, 3]. This is the case of A. triquetrum that its distribution enables the renewal and supply of new seedlings in cultivation systems, if production processes are implemented [4]

  • The overall epibiont community associated with A. triquetrum was divided into 21 taxonomic groups, with only four of those groups showing unique to either summer or winter season (Table 1)

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Summary

Introduction

The increasing demand for macroalgal biomass has stimulated a global expansion of macroalgal farming [1] It has encouraged research on species that are not yet domesticated but contain components of interest, for the biomedical and pharmacological industry [2, 3]. This is the case of A. triquetrum that its distribution enables the renewal and supply of new seedlings in cultivation systems, if production processes are implemented [4]. While the exploitation of macroalgae gains momentum, fundamental knowledge gaps related to ecological interactions emerge. One example is the limited information regarding epibiotic interactions between farmed macroalgae and macroinvertebrates

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