A guide for planners and managers - IUCN
A guide for planners and managers - IUCN
A guide for planners and managers - IUCN
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166 MARINE AND COASTAL<br />
PROTECTED AREAS<br />
Johannes (1975) states that fringing reefs “are self-repairing breakwaters which<br />
permit the continued existence of about 400 atolls <strong>and</strong> numerous other low tropical<br />
isl<strong>and</strong>s, as well as preserve thous<strong>and</strong>s of miles of continental coastlines.” Entire<br />
isl<strong>and</strong> archipelagos owe their existence to the reef-building processes of past millennia<br />
<strong>and</strong> the protective role of living sea-level reefs. In the Indian Ocean, <strong>for</strong> example, 77<br />
percent of the isolated isl<strong>and</strong>s <strong>and</strong> isl<strong>and</strong> archipelagos are built exclusively of reef<br />
depositions, <strong>and</strong> 18 percent have coral isl<strong>and</strong>s in addition to the principal isl<strong>and</strong> type<br />
(Figure II-5). The Maldives Archipelago alone comprises 20 atolls <strong>and</strong> about 2,000<br />
coral isl<strong>and</strong>s. Coral isl<strong>and</strong>s are valuable <strong>for</strong> tourist sites, permanent settlement,<br />
plantations (notably coconut <strong>and</strong> papaya), <strong>and</strong> a refuge <strong>for</strong> fishermen in stormy<br />
weather, temporary bases <strong>for</strong> itinerant fishermen, <strong>and</strong> recreation areas. They also provide<br />
sanctuaries to a number of species, including seabirds <strong>and</strong> turtles.<br />
FIGURE II-5.<br />
A satellite-eye view of Salomon Atoll (Indian Ocean) as digitally<br />
interpreted by computer graphing. Notice the characteristic ringlike<br />
reef on which isl<strong>and</strong>s <strong>for</strong>m, the central lagoon, <strong>and</strong> the sheer seaward<br />
slope of atolls.<br />
In summary, coral reefs<br />
are utilized <strong>for</strong> subsistence,<br />
income generation, research,<br />
<strong>and</strong> recreation. Their uses can<br />
be classified as either extractive<br />
or non-extractive. Extractive<br />
uses include the harvest of edible<br />
species (fishes, crabs, lobsters,<br />
snails, clams, octopus, sea<br />
cucumbers, sea urchins, <strong>and</strong><br />
turtles), the harvest of ornamental<br />
products (pearls, coral,<br />
echinoderms. molluscs, <strong>and</strong><br />
turtles), <strong>and</strong> the harvest of industrial<br />
products (bulk coral,<br />
sponges. <strong>and</strong> giant clams). Nonextractive<br />
uses include recre-<br />
ation, science <strong>and</strong> education, tourism, <strong>and</strong> shore protection. Cesar (1996), Cesar et al.<br />
(1997), <strong>and</strong> Spurgeon <strong>and</strong> Aylward (1992) have attempted economic valuation of these<br />
reef products <strong>and</strong> services.<br />
1.3 Threats from Human Activities<br />
Coral reefs are in trouble from both natural <strong>and</strong> human causes. The literature<br />
abounds with many cases of damage from careless development (see, <strong>for</strong> example,<br />
Bryant et al., 1998; Endean, 1976; Johannes, 1975; Salvat, 1974, 1978, 1987a;<br />
UNEP/<strong>IUCN</strong>, 1988; Wells <strong>and</strong> Hanna, 1992; Wilkinson, 1998). Specific examples are<br />
discussed in the following paragraphs.<br />
After the mining of coral reefs on high energy shorelines on the east coast of<br />
Sri Lanka (Figure II-6) the shoreline eroded, causing trees <strong>and</strong> coconut palms to fall