Abstract

Resilience is the ability of an ecosystem to recover from disturbance without loss of essential function. Seagrass ecosystems are key marine and estuarine habitats that are under threat from a variety of natural and anthropogenic disturbances. The ability of these ecosystems to recovery from disturbance will to a large extent depend on the internsity and scale of the disturbance, and the relative importance of sexual versus asexual reproduction within populations. Here, we investigated the resilience of Zostera muelleri seagrass (Syn. Zostera capricorni) to small-scale disturbances at four locations in Lake Macquarie – Australia's largest coastal lake – and monitored recovery over a 65-week period. Resilience of Z. muelleri varied significantly with disturbance intensity; Z. muelleri recovered rapidly (within 2 weeks) from low-intensity disturbance (shoot loss), and rates of recovery appeared related to initial shoot length. Recovery via rhizome encroachment (asexual regeneration) from high-intensity disturbance (loss of entire plant) varied among locations, ranging from 18-35 weeks, whereas the ability to recover was apparently lost (at least within the time frame of this study) when recovery depended on sexual regeneration, suggesting that seeds do not provide a mechanism of recovery against intense small-scale disturbances. The lack of sexual recruits into disturbed sites is surprising as our initial surveys of genotypic diversity (using nine polymorphic microsatellite loci) at these location indicate that populations are maintained by a mix of sexual and asexual reproduction (genotypic diversity [R] varied from 0.24 to 0.44), and populations consisted of a mosaic of genotypes with on average 3.6 unique multilocus genotypes per 300 mm diameter plot. We therefore conclude that Z. muelleri populations within Lake Macquarie rely on clonal growth to recover from small-scale disturbances and that ongoing sexual recruitment by seeds into established seagrass beds (as opposed to bare areas arising from disturbance) must be the mechanism responsible for maintaining the observed mixed genetic composition of Z. muelleri seagrass meadows.

Highlights

  • There is still major uncertainty about how climate change will affect marine ecosystems, largely because of a lack of understanding of the processes that provide insurance against environmental change, that is ecosystem resilience

  • Levels of genotypic diversity (R) indicated that the relative importance of sexual and asexual reproduction varied across locations

  • Valentine and Point Wolstoncroft displayed the lowest levels of genotypic diversity (R = 0.24 and R = 0.27 respectively), while Wangi and Sunshine displayed almost twice the amount of genotypic diversity seen at other locations (R = 0.44 at both locations)

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Summary

Introduction

There is still major uncertainty about how climate change will affect marine ecosystems, largely because of a lack of understanding of the processes that provide insurance against environmental change, that is ecosystem resilience. Resilience refers to the capacity of ecosystems to cope with disturbance, without switching to an alternative (and undesirable) stable state, sometimes referred to as a “phase or regime shift.”. Many ecologists believe that if the factors that mediate resilience for a given ecosystem can be predicted, monitored, and modified, desired ecosystem states could be maintained in the face of increasing environmental change (Folke et al 2004). There is currently a global push toward understanding the mechanisms that underpin resilience in seagrass a 2014 The Authors.

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