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#Status of Coral Reefs 2002 - International Coral Reef Action Network

#Status of Coral Reefs 2002 - International Coral Reef Action Network

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Status <strong>of</strong> <strong>Coral</strong> <strong><strong>Reef</strong>s</strong> in the Northern Caribbean and Atlantic Node <strong>of</strong> the GCRMN<br />

<strong>of</strong>fshore reefs that are less impacted by anthropogenic effects. These include the<br />

Montecristi barrier reef and the Silver Banks with mean coral cover approximating 40-50%.<br />

Haiti<br />

There is virtually no monitoring due to the political impasse between the Haitian<br />

government and the international community about funding activities, including<br />

environmental activities. Presumably the reefs have suffered from the recent Caribbeanwide<br />

mortalities from coral bleaching and disease, as well as the effects <strong>of</strong> extreme<br />

deforestation, over-fishing and local pollution. Over-fishing continues unchecked and the<br />

lack <strong>of</strong> herbivores means macroalgal growth is not controlled and smothers corals. There<br />

is obvious damage from urban run<strong>of</strong>f from Port-au-Prince.<br />

Jamaica<br />

The reefs continue to show symptoms <strong>of</strong> stress. Low coral cover and dominance by<br />

macroalgae is clearly evident, particularly on shallow reefs, where coral cover ranges from<br />

2 - 20%. However, deeper reefs are in better condition. A CARICOMP monitoring site in<br />

Discovery Bay at 8m, shows a slight increase in coral cover from 9% to 12-14% in 10<br />

years. Parallel <strong>Reef</strong>Check surveys suggest slightly higher cover. Densities <strong>of</strong> the sea urchin<br />

(Diadema antillarum) increased until 1999, but have since declined. There are, however,<br />

encouraging signs <strong>of</strong> some recovery, with good coral recruitment on shallow reefs. In the<br />

Negril Marine Park, reefs have remained stable over the past 5 years and are generally in<br />

poor condition. Recovery is impeded by seasonal storms, constant fishing (including spear<br />

fishing, pot fishing and seine net fishing), heavy algal cover, frequent diving and<br />

snorkelling by tourists and locals, and sedimentation. The biggest problem is<br />

eutrophication and data from the Negril <strong>Coral</strong> <strong>Reef</strong> Preservation Society (NCRPS) confirm<br />

that macroalgal biomass on the reefs in Negril is at critical levels, particularly on<br />

reefs near the mouth <strong>of</strong> the South Negril River. Sewage and land run-<strong>of</strong>f carrying<br />

agricultural fertilisers contribute to high nutrient loadings around Negril. Live coral cover<br />

remains low, between 5 and 12% in 2000 as does coral recruitment. There are, however,<br />

some reefs outside most <strong>of</strong> the coastal stresses that are in reasonably good condition. <strong>Reef</strong><br />

Check surveys in Bloody Bay Negril suggest 30-40% coral cover, with many healthy<br />

gorgonians, but very few fish were seen confirming that over-fishing continues to be a<br />

major problem. Beach erosion in Negril continues without any immediate solution, and<br />

in future, the rapid deterioration <strong>of</strong> the reefs in the Negril Marine Park may reduce their<br />

ability to protect the shoreline from erosion.<br />

South coast reefs, particularly those near high population centres, are similarly stressed e.g.<br />

coral cover near Kingston Harbour varied from 7.3% at South East Cay to 21.4% at<br />

Rackhams Cay (average 15%). Density <strong>of</strong> coral recruits ranged from 1 to 6.4 individuals per<br />

m 2 , and the incidence <strong>of</strong> coral bleaching was 1.9 to 16.7%. There were signs <strong>of</strong> slow recovery<br />

<strong>of</strong> Diadema antillarum populations. <strong><strong>Reef</strong>s</strong> around the <strong>of</strong>fshore islands in the Portland Bight<br />

Protected Area are in better condition, though impacted by siltation and some algal<br />

overgrowth. Visual estimates <strong>of</strong> coral cover at Pigeon Island in 2001 and <strong>2002</strong> were >20% and<br />

coral recruits <strong>of</strong> different species e.g. Agaricia, Siderastrea and Acropora (cervicornis) were<br />

observed. There were low levels <strong>of</strong> disease (1.4%) and bleaching (1.4%). Again, fishes were<br />

small and scarce with no large predators. The <strong>of</strong>fshore reefs at the Morant and Pedro Cays are<br />

relatively inaccessible and less impacted than inshore reefs, but there are no recent data.<br />

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