Abstract

Abstract Designated using a Statutory Instrument in 2008, Lyme Bay marine‐protected area (MPA) is the UK's first and largest example of an ambitious, whole‐site approach to management, to recover and protect reef biodiversity. The whole‐site approach applies consistent management, in this case excluding bottom towed fishing, across the full 206 km2 extent of the MPA, thus protecting a mosaic of reef‐associated habitats from regular damage, while still allowing less destructive fishing methods, such as static gear, rod and line, and diving. To assess the effectiveness of this management strategy for mobile taxa and the sustainability for those taxa that continue to be targeted, Exploited and Non‐Exploited species' populations were compared inside the MPA, relative to open control sites spanning 11 of the 12 years of designation. baited remote underwater video systems (BRUVs) were deployed annually to assess mobile benthic and demersal fauna. Overall, the number of taxa significantly increased in the MPA relative to the open controls while total abundance increased in both treatments. Exploited fish showed increases in number of taxa (430%) and total abundance (370%) inside the MPA over 11 years. Likewise, but to a lesser degree in the open controls, number of taxa of commercially Exploited fish increased over time, potentially showing ‘spillover’ effects from the MPA. Non‐Exploited fish did not show such changes. Regardless of constituting the majority of the fishery value, highly valuable Exploited invertebrates showed no significant changes over time. Synthesis and applications. The Lyme Bay marine‐protected area shows importance of protecting a whole site, comprising mosaics of different benthic habitats, through protection of sessile organisms that contribute to essential fish habitats. This Ecosystem Approach to Fisheries Management can benefit and maintain sustainable fisheries and species of conservation importance.

Highlights

  • The implementation of marine-­protected areas (MPAs) to conserve and protect marine biodiversity and aid fishery management has increased rapidly over the last 25 years (Da Silva et al, 2015; Halpern et al, 2010)

  • To assess the effectiveness of this management strategy for mobile taxa and the sustainability for those taxa that continue to be targeted, Exploited and Non-­ Exploited species' populations were compared inside the MPA, relative to open control sites spanning 11 of the 12 years of designation. baited remote underwater video systems (BRUVs) were deployed annually to assess mobile benthic and demersal fauna

  • The number of taxa significantly increased in the MPA relative to the open controls while total abundance increased in both treatments

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Summary

| INTRODUCTION

The implementation of marine-­protected areas (MPAs) to conserve and protect marine biodiversity and aid fishery management has increased rapidly over the last 25 years (Da Silva et al, 2015; Halpern et al, 2010). This form of management limits recovery potential as the presence, extent and condition of features are required to be evidenced This ‘feature-­based’ management, which is the most common approach employed within UK waters, means that out of 66,507 km of seabed within UK MPAs only 4,811 km (7.2%) is protected from the most destructive fishing methods (Marine Conservation Society & Marine Mapping Ltd., 2019)—­just the habitat or species ‘feature’ for which the MPA is designated, not the rest of the seabed area. The most destructive fishing activities, trawling and scallop dredging, were excluded from a mosaic of habitats (~206 km2) while static gear and diving were still permitted This created both the Lyme Bay MPA and the rare opportunity to study the effect of the whole-­site approach for the first time over such a large temporal (11 years) and spatial scale (>200 km). The following hypotheses were tested: 5. When considered separately, the total abundance of Exploited and Non-­Exploited species all increase over time in the MPA, relative to areas that remain open to bottom towed fishing

| MATERIALS AND METHODS
Findings
| DISCUSSION
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