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Jackson2013-Status and Trendsof Caribbean Coral Reefs

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Fig. 29.2 Average percent cover<br />

of live corals (A) <strong>and</strong> macroalgae<br />

(B), density of Diadema antillarum<br />

(C), <strong>and</strong> parrotfishes <strong>and</strong> groupers<br />

biomass (D) in St. Lucia. Dotted<br />

line represents the average of<br />

<strong>Caribbean</strong> data collected for this<br />

report. (Codes same as in Table<br />

29.1 <strong>and</strong> Figure 29.1)<br />

Timeline<br />

1955: Hurricane Janet<br />

1950s-1970s: <strong>Reefs</strong> ecosystems, as well as mangroves <strong>and</strong> seagrass beds in a healthy state; coral diversity <strong>and</strong> cover<br />

are high, with relatively few <strong>and</strong> low abundance of macroalgae; healthy populations of reef herbivores<br />

such as sea urchins Diadema; well balanced food chain with wide size ranges in various fish species<br />

<strong>and</strong> healthy levels of abundance of top predators (e.g., groupers; large snappers; barracuda’s etc.).<br />

Fishing fleet focused mainly on near-shore fishing using wooden transoms <strong>and</strong> canoes propelled by sail,<br />

oar <strong>and</strong> small outboard engines.<br />

1960: Hurricane Abby<br />

1963: Hurricane Edith<br />

1975-1980: Transition from the traditional wooden canoe to the more stable, fiberglass pirogue (mostly 12–25 feet)<br />

with outboard engines of 75–100 Hp.<br />

1980: Hurricane Allen<br />

1980s-1990s: Change of focus for fishing fleet from near-shore fishing to offshore fishing for migratory pelagic fishes<br />

such as tunas, dolphinfish <strong>and</strong> wahoo (which started to contribute approximately 65-75% to the annual<br />

catch).<br />

1983: Mass mortality of Diadema antillarum on local reefs (over 65% mortality)<br />

1980 – 1995: significant expansion of tourism (including cruise ship arrivals <strong>and</strong> mass water-based tourism in certain<br />

locations) <strong>and</strong> banana cultivation; associated increased levels of <strong>and</strong> impacts from sedimentation in<br />

coastal areas which led to significant reef decline in many coastal areas (particularly northwest to central<br />

west coastal areas).<br />

1984-1994: new fisheries laws enacted with mesh size restrictions for traps <strong>and</strong> nets; size limits <strong>and</strong> close seasons<br />

for many species, e.g., lobster, conch, turtles <strong>and</strong> sea urchins; prohibitions on use of toxins <strong>and</strong><br />

dynamite; restrictions on use of spearguns, etc.<br />

1986: a number of marine reserves established (many coral reefs; 2 turtle nesting beaches; several mangrove<br />

areas) but no demarcation <strong>and</strong> little day-to-day management put in place following their declaration.<br />

1990-2012: Fish Aggregating Devises tested <strong>and</strong> implemented as a means of attracting fishers away from reefs<br />

which were becoming more stressed <strong>and</strong> degraded by a combination of increased sedimentation, poor<br />

fishing practices; large–scale water-based tourism, other forms of coastal pollution <strong>and</strong> successive<br />

severe weather impacts.<br />

1992-1997: influx into the fisheries sector due to declines in the banana industry; resultant increasing fishing<br />

pressure in coastal areas, particularly during the low season when migratory pelagic fish species are not<br />

readily available (approximately July to December).<br />

1994: Soufriere Marine Management Area is established: an 11km stretch of coastal marine space with<br />

marine reserves, multiple use areas, yacht mooring zones <strong>and</strong> recreational zones created to bring about<br />

integrated resource use <strong>and</strong> conflict resolution, sustainable resource use <strong>and</strong> reef recovery.<br />

STATUS AND TRENDS OF CARIBBEAN CORAL REEFS: 1969-2012<br />

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