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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

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<strong>Status</strong> <strong>of</strong> Coral Reefs <strong>in</strong> the <strong>Caribbean</strong> <strong>after</strong> Bleach<strong>in</strong>g <strong>and</strong> Hurricanes <strong>of</strong> <strong>2005</strong>Some climate change impacts, particularly <strong>in</strong> comb<strong>in</strong>ation with other <strong>in</strong>fluences, will likelyreduce the overall resilience <strong>of</strong> <strong>coral</strong> <strong>reefs</strong>. Changes <strong>in</strong> a <strong>coral</strong> community (such as reducedbiodiversity) may severely underm<strong>in</strong>e system resilience, result<strong>in</strong>g <strong>in</strong> a phase shift to a non<strong>coral</strong>reef community. For example, the loss <strong>of</strong> some fish <strong>and</strong> <strong>in</strong>vertebrates may leave a <strong>coral</strong>reef more susceptible to episodic outbreaks <strong>of</strong> pests or <strong>in</strong>vad<strong>in</strong>g species. Effects like this tendto be unpredictable, but such unpredicted changes are likely to <strong>in</strong>crease.Climate change also affects <strong>coral</strong> <strong>reefs</strong> <strong>in</strong> another, fundamental way that is unique to thisecosystem; that is the effects on the geological reef structure itself. Reduced <strong>coral</strong> cover (e.g.from <strong>coral</strong> <strong>bleach<strong>in</strong>g</strong>) coupled with lowered calcification rates <strong>and</strong> <strong>in</strong>creased dissolution rates(ocean acidification) will reduce the net calcium carbonate production rates on <strong>reefs</strong>. By theend <strong>of</strong> this century, the overall balance <strong>of</strong> carbonate production on many <strong>reefs</strong> is expected todecl<strong>in</strong>e to the po<strong>in</strong>t where reef-build<strong>in</strong>g may cease or reverse. In addition, any ecosystems thatare <strong>in</strong>fluenced by the reef structure <strong>and</strong> reef sediment production will also be affected. Thesecould <strong>in</strong>clude mangroves, seagrass beds, <strong>and</strong> low-ly<strong>in</strong>g <strong>coral</strong> cays. It might also have significantimplications for human <strong>in</strong>frastructure on coastl<strong>in</strong>es protected by <strong>coral</strong> <strong>reefs</strong>.Aga<strong>in</strong>st the background <strong>of</strong> these dire predictions fac<strong>in</strong>g <strong>coral</strong> <strong>reefs</strong>, implement<strong>in</strong>g management<strong>of</strong> local damage may seem irrelevant unless the current growth <strong>in</strong> greenhouse gas emissionsis constra<strong>in</strong>ed. Even with drastic reductions <strong>in</strong> CO 2concentrations, there will be changes<strong>and</strong> challenges for <strong>coral</strong> <strong>reefs</strong>. However, <strong>after</strong> the massive <strong>coral</strong> <strong>bleach<strong>in</strong>g</strong> <strong>in</strong> 1998, <strong>coral</strong> <strong>reefs</strong>recovered better <strong>and</strong> more rapidly where stresses related to poor water quality <strong>and</strong> overfish<strong>in</strong>gwere well managed. For example, where graz<strong>in</strong>g fish are reta<strong>in</strong>ed on a reef, <strong>coral</strong>s willrepopulate damaged areas 2–3 times faster than on over-fished <strong>reefs</strong>; similarly, growth rates<strong>of</strong> <strong>coral</strong>s are faster <strong>in</strong> non-polluted waters. Manag<strong>in</strong>g local stresses on <strong>reefs</strong> may not preventdamage from climate change, however it will enhance recovery.Recent evidence <strong>in</strong>dicates it is imperative that there is strong action on reduc<strong>in</strong>g greenhouseemissions to ensure that we don’t exceed much more than 450-500 ppm CO 2<strong>in</strong> the atmosphere.Any response, however, must <strong>in</strong>clude local strategies to <strong>in</strong>crease the effective management <strong>of</strong>local stresses, such as decl<strong>in</strong><strong>in</strong>g water quality <strong>and</strong> overfish<strong>in</strong>g, damag<strong>in</strong>g <strong>coral</strong> <strong>reefs</strong>. Reefs willpersist longer under the stresses <strong>of</strong> the next 50–100 years if they are given the best chance <strong>of</strong>recover<strong>in</strong>g from the <strong>in</strong>evitable ecological shocks; this will ‘buy time’. These two approaches,decreas<strong>in</strong>g emissions <strong>and</strong> <strong>in</strong>creas<strong>in</strong>g protective management, are an <strong>in</strong>tegral part <strong>of</strong> effectivelyaddress<strong>in</strong>g the current <strong>coral</strong> reef crisis <strong>and</strong> are discussed <strong>in</strong> Chapter 10, p. 115.Au t h o r Co n ta c t sJoan Kleypas, National Center for Atmospheric Research Boulder, Colorado, USA, kleypas@ucar.edu; Ove Hoegh-Guldberg, Centre for Mar<strong>in</strong>e Studies, University <strong>of</strong> Queensl<strong>and</strong>, Australia.oveh@uq.edu.auReferencesF<strong>in</strong>e M, Tchernov D (2007). Scleract<strong>in</strong>ian <strong>coral</strong> species survive <strong>and</strong> recover fromdecalcification. Science 315:1811.Hoegh-Guldberg O, Mumby PJ, Hooten AJ, Steneck RS, Greenfield P, Gomez E, Harvell DR,Sale PF, Edwards AJ, Caldeira K, Knowlton N, Eak<strong>in</strong> CM, Iglesias-Prieto R, MuthigaN, Bradbury RH, Dubi A, Hatziolos ME (2007). Coral <strong>reefs</strong> under rapid climate change<strong>and</strong> ocean acidification. Science 318 (5857): 1737-1742.28

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