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Status of Caribbean coral reefs after bleaching and hurricanes in 2005

Status of Caribbean coral reefs after bleaching and hurricanes in 2005

Status of Caribbean coral reefs after bleaching and hurricanes in 2005

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Manag<strong>in</strong>g for Mass Coral Bleach<strong>in</strong>g: Strategies for Support<strong>in</strong>g Socio–ecological Resilienceareas along prevail<strong>in</strong>g, larvae-carry<strong>in</strong>g currents can replenish downstream <strong>reefs</strong>,<strong>in</strong>creas<strong>in</strong>g the probability <strong>of</strong> recovery at multiple <strong>coral</strong> reef sites. Non-reef areasadjacent to highly-protected <strong>reefs</strong> may also warrant <strong>in</strong>creased protection becausethey can become stag<strong>in</strong>g areas for <strong>coral</strong> recruits as they move between <strong>reefs</strong>.zx Good ecosystem condition – High <strong>coral</strong> cover, abundant fish populations, <strong>and</strong> goodwater quality are all elements <strong>of</strong> <strong>coral</strong> reef health that support recovery. Ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g,enhanc<strong>in</strong>g, or restor<strong>in</strong>g these valuable characteristics through management<strong>in</strong>terventions are easier to achieve <strong>in</strong> some areas than others, because <strong>of</strong> variousattributes <strong>of</strong> site location <strong>and</strong> use. In develop<strong>in</strong>g MPA networks, it is useful toconsider whether additional management protection can be effective <strong>in</strong> ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>gthese resilience-support<strong>in</strong>g qualities <strong>of</strong> ecosystem condition.These pr<strong>in</strong>ciples are already be<strong>in</strong>g implemented <strong>in</strong>to MPA networks around the world,<strong>in</strong>clud<strong>in</strong>g: Palau; the British Virg<strong>in</strong> Isl<strong>and</strong>s; Belize; the Seychelles; Yemen; <strong>and</strong> the Maldives.The Nature Conservancy’s Reef Resilience (R2) Toolkit (8) or website (www.reefresilience.org)has a more detailed discussion <strong>of</strong> how to identify resilient areas <strong>and</strong> <strong>in</strong>corporate these areas<strong>in</strong>to MPA design.Strategy 3. Reduce local stressors to build <strong>coral</strong> tolerance to <strong>bleach<strong>in</strong>g</strong>.Global climate change will add stress to <strong>coral</strong> <strong>reefs</strong>; therefore the removal <strong>of</strong> local stressors canhelp <strong>coral</strong>s respond to these new, difficult conditions. Remov<strong>in</strong>g chronic local stressors causedby <strong>in</strong>tensive tourism use, water pollution, or over-fish<strong>in</strong>g can <strong>in</strong>crease <strong>coral</strong> reef health <strong>and</strong>lipid levels. Corals with higher energy reserves are more likely to survive a <strong>bleach<strong>in</strong>g</strong> event.Removal <strong>of</strong> acute stressors to <strong>coral</strong>s dur<strong>in</strong>g <strong>bleach<strong>in</strong>g</strong> events is also likely to <strong>in</strong>crease theirability to survive. Bleached <strong>coral</strong>s are extremely stressed <strong>and</strong> have a reduced capacity forma<strong>in</strong>tenance <strong>of</strong> essential functions, such as <strong>in</strong>jury repair, resistance to pathogens, <strong>and</strong> defenceaga<strong>in</strong>st competitors. A stressed <strong>coral</strong> is less capable <strong>of</strong> recover<strong>in</strong>g from physical <strong>in</strong>juries causedby careless snorkel<strong>in</strong>g, div<strong>in</strong>g, <strong>and</strong> boat anchor<strong>in</strong>g. Repair <strong>of</strong> even m<strong>in</strong>or tissue damage maybe h<strong>in</strong>dered for a stressed <strong>coral</strong>, thereby <strong>in</strong>creas<strong>in</strong>g the risk <strong>of</strong> <strong>in</strong>fection or overgrowth bycompet<strong>in</strong>g organisms. Acute <strong>in</strong>creases <strong>in</strong> sediments <strong>and</strong> pollutants from coastal development ordredg<strong>in</strong>g will deliver additional stress to <strong>coral</strong>s that must clear sediment from colony surfaces,wast<strong>in</strong>g precious physiological resources. Bleached <strong>coral</strong>s are also less effective at defend<strong>in</strong>gaga<strong>in</strong>st <strong>in</strong>vasion by microalgae or compet<strong>in</strong>g with macroalgae. These <strong>coral</strong> competitors benefitfrom <strong>in</strong>creases <strong>in</strong> nutrients or reductions <strong>in</strong> the herbivorous fish populations that consumethem. Therefore, management can promote <strong>coral</strong> survival dur<strong>in</strong>g mass <strong>bleach<strong>in</strong>g</strong> events bylimit<strong>in</strong>g damage from recreation, degraded water quality, <strong>and</strong> fish<strong>in</strong>g pressures.Strategy 4. Protect, ma<strong>in</strong>ta<strong>in</strong> or enhance the conditions that promote ecosystem recovery.Coral cover, water quality, <strong>and</strong> herbivorous fish abundance are critical <strong>in</strong> determ<strong>in</strong><strong>in</strong>g reefrecovery through their <strong>in</strong>fluence on processes, <strong>in</strong>clud<strong>in</strong>g: larval supply; availability <strong>of</strong>substrate for settlement; <strong>coral</strong> recruitment rates; <strong>and</strong> survival <strong>of</strong> juvenile <strong>coral</strong>s. Traditionalmanagement strategies may be based on the assumption that <strong>reefs</strong> are likely to cont<strong>in</strong>ue <strong>in</strong>relatively stable condition. As <strong>reefs</strong> spend more time <strong>in</strong> recovery mode, management targetsmay need to become more conservative to achieve satisfactory water quality, fish abundances,<strong>and</strong> <strong>coral</strong> cover. For example, water quality st<strong>and</strong>ards <strong>and</strong> fishery management regimes should123

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