Abstract

The recovery of communities of predatory fishes within a no‐take marine reserve after the eradication of illegal fishing provides an opportunity to examine the role of sharks and other large‐bodied mesopredatory fishes in structuring reef fish communities. We used baited remote underwater video stations to investigate whether an increase in sharks was associated with a change in structure of the mesopredatory fish community at Ashmore Reef, Western Australia. We found an almost fourfold increase in shark abundance in reef habitat from 0.64 hr−1 ± 0.15 SE in 2004, when Ashmore Reef was being fished illegally, to 2.45 hr−1 ± 0.37 in 2016, after eight years of full‐time enforcement of the reserve. Shark recovery in reef habitat was accompanied by a two and a half‐fold decline in the abundance of small mesopredatory fishes (≤50 cm TL) (14.00 hr−1 ± 3.79 to 5.6 hr−1 ± 1.20) and a concomitant increase in large mesopredatory fishes (≥100 cm TL) from 1.82 hr−1 ± 0.48 to 4.27 hr−1 ± 0.93. In contrast, near‐reef habitats showed an increase in abundance of large mesopredatory fishes between years (2.00 hr−1 ± 0.65 to 4.56 hr−1 ± 1.11), although only smaller increases in sharks (0.67 hr−1 ± 0.25 to 1.22 hr−1 ± 0.34) and smaller mesopredatory fishes. Although the abundance of most mesopredatory groups increased with recovery from fishing, we suggest that the large decline of small mesopredatory fish in reef habitat was mostly due to higher predation pressure following the increase in sharks and large mesopredatory fishes. At the regional scale, the structure of fished communities at Ashmore Reef in 2004 resembled those of present day Scott Reefs, where fishing still continues today. In 2016, Ashmore fish communities resembled those of the Rowley Shoals, which have been protected from fishing for decades.

Highlights

  • Large predators can structure ecosystems in terrestrial and aquatic environments (Estes et al, 2011) through both consumption of prey and by influencing prey distribution and behavior (Creel & Christianson, 2008; Heithaus, Wirsing, Burkholder, Thomson, & Dill, 2009; Ripple & Beschta, 2004)

  • Notably coral reefs, evidence for the role of large predators in the top‐down regulation of ecosystems remains contentious (Casey et al, 2017), al‐ though studies have indicated that important processes such as her‐ bivory can be suppressed around reefs through the fear of predation (Madin, Madin, & Booth, 2011; Rizzari, Frisch, Hoey, & McCormick, 2014)

  • Changes in the mesopredatory fish communities were assessed for Ashmore Reef between habi‐ tats and years using a principal component analysis (PCA) on scaled MaxN data for species that occurred on ≥10% of deployments

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Summary

| INTRODUCTION

Large predators can structure ecosystems in terrestrial and aquatic environments (Estes et al, 2011) through both consumption of prey and by influencing prey distribution and behavior (Creel & Christianson, 2008; Heithaus, Wirsing, Burkholder, Thomson, & Dill, 2009; Ripple & Beschta, 2004). Many populations of reef sharks are declining (e.g., Graham, Spalding, & Sheppard, 2010; Robbins, Hisano, Connolly, & Choat, 2006; Ward‐Paige, Mora, et al, 2010), in a few circumstances, changes in management strategies or better enforcement of existing regulations have allowed numbers of reef sharks to recover (e.g., Espinoza, Cappo, Heupel, Tobin, & Simpfendorfer, 2014; Speed, Cappo, & Meekan, 2018) These offer a unique opportunity to gain insights into the importance of sharks in reef environments and a means to test predictions generated by spatial comparisons through comparisons of the structure of fish communities prior to and after recovery of shark populations. Contrasts between these habitats may be important given the growing evidence that reefs sharks and other predatory fish species can consume non‐reef‐based prey (Frisch, Ireland, & Baker, 2014; Frisch et al, 2016; McCauley et al, 2012)

| METHODS
| DISCUSSION
Findings
CONFLICT OF INTEREST
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