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Status of Coral Reefs of the World 2000

Status of Coral Reefs of the World 2000.pdf

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<strong>Status</strong> <strong>of</strong> <strong>Coral</strong> <strong>Reefs</strong> <strong>of</strong> <strong>the</strong> <strong>World</strong>: <strong>2000</strong><br />

<strong>2000</strong>. Some reefs that are showing significant recovery were already severely impacted by<br />

fishing and collecting, and occur in relatively marginal reef flat environments. This suggests<br />

that pre-exposure to temperature and o<strong>the</strong>r stresses may be a positive adaptation and<br />

result in faster recovery in some areas. However in o<strong>the</strong>rs, damage to <strong>the</strong> reefs from overfishing<br />

and overgrowth by fleshy algae may have been delaying coral and reef recovery.<br />

Since <strong>the</strong>se observations are based on reefs in early stages <strong>of</strong> succession no definitive<br />

conclusions can be made.<br />

Crown-<strong>of</strong>-thorns Starfish (COTS)<br />

These starfish (Acanthaster planci) have been a major threat to <strong>the</strong> reefs throughout<br />

Tanzania, Mozambique and South Africa during <strong>the</strong> past decade. Damage to deeper reefs<br />

in South Africa from COTS since 1990 appears to be shifting <strong>the</strong> balance towards s<strong>of</strong>t<br />

corals, because <strong>the</strong> starfish target <strong>the</strong> hard corals.<br />

Fishing<br />

Excessive and destructive fishing in East Africa was <strong>the</strong> major anthropogenic problem for<br />

<strong>the</strong> reefs throughout <strong>the</strong> 1990s; only surpassed in impact by <strong>the</strong> El Niño bleaching event<br />

took which took over as <strong>the</strong> major threat in this region. Damaging fishing practices include:<br />

dynamite; pull-seine nets; poisons; over-exploitation <strong>of</strong> juveniles and small fish (direct<br />

targets and by-catch); and local intensive harvesting <strong>of</strong> specific resources (octopus,<br />

shellfish, and lobster). Sea cucumber populations have crashed following <strong>the</strong> introduction<br />

<strong>of</strong> export fisheries. Since <strong>the</strong> last status report <strong>of</strong> 1998, fishing pressures have not<br />

decreased in any country, yet <strong>the</strong>re have been some specific improvements, notably:<br />

• In Tanzania, increased public pressure by communities and NGOs has led to: a)<br />

effective reduction <strong>of</strong> dynamite fishing in key areas (Tanga, Mafia, Songosongo),<br />

and b) delayed implementation <strong>of</strong> a controversial aquaculture development<br />

project in <strong>the</strong> Rufiji Delta with its ultimate collapse in <strong>2000</strong>;<br />

• In Mozambique, <strong>the</strong>re has been a ministerial ban on aquarium fish collection pending<br />

a study on <strong>the</strong> potential impacts and sustainable management <strong>of</strong> <strong>the</strong> trade; and<br />

• There has been increasing efforts in all countries to involve and empower local<br />

users in monitoring and management e.g. in Tanga and Misali (Tanzania), Kiunga<br />

and Diani (Kenya), and Angoche (Mozambique).<br />

Tourism<br />

Coastal tourism in all <strong>the</strong> East African countries depends on healthy coral reefs as <strong>the</strong><br />

primary attraction, however, increasing development <strong>of</strong> tourist facilities is also threatening<br />

<strong>the</strong> reefs. All countries are starting to promote ‘ecologically friendly’ and sustainable<br />

tourism developments, which include smaller, more exclusive hotels and resorts, diving<br />

and wilderness-oriented activities, as well as co-management <strong>of</strong> <strong>the</strong> reef resources<br />

between communities, developers and government. Some studies on tourism impacts on<br />

<strong>the</strong> physical, biological and socioeconomic status <strong>of</strong> coral reef areas have been<br />

conducted, however <strong>the</strong>re are large gaps in <strong>the</strong> coverage <strong>of</strong> studies and in implementation<br />

<strong>of</strong> recommended actions.<br />

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