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A guide for planners and managers - IUCN

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114 MARINE AND COASTAL<br />

PROTECTED AREAS<br />

Box I-10. Everglades National Park<br />

The state of Florida (USA) provides several useful examples of large-scale<br />

preservation. The Everglades National Park was established in south Florida in 1947<br />

<strong>and</strong> currently encompasses more than 500,000 ha of l<strong>and</strong> <strong>and</strong> water. Although much<br />

of this area is composed of upl<strong>and</strong> plant communities, a significant portion is mangrove,<br />

sea grass beds, <strong>and</strong> coastal marshes. All of these habitat types provide nursery areas <strong>for</strong><br />

the extensive commercial <strong>and</strong> sport fisheries that operate in contiguous coastal waters.<br />

The great strength of Everglades National Park is that it includes almost the<br />

entire gradient from upl<strong>and</strong> freshwater, through the estuary, to offshore many kilometers.<br />

The nearby Biscayne National Monument similarly includes coastal wetl<strong>and</strong>s <strong>and</strong><br />

mangroves, sea grass <strong>and</strong> macroalgae beds, barrier isl<strong>and</strong>s <strong>and</strong> passes, <strong>and</strong> offshore coral<br />

reefs. Together these two MPAs are designed to protect <strong>and</strong> nurture many commercial<br />

<strong>and</strong> recreational species like the gray snapper in all the various stages of their lives. The<br />

Everglades system also guarantees unimpeded natural production of detritus, which <strong>for</strong>ms<br />

the basis of a complex food web that supports stocks of fishes.<br />

Un<strong>for</strong>tunately, some factors cannot be totally controlled, even in a preserved<br />

area as large as the Everglades National Park (Morehead, 1984). For example, the<br />

watershed draining into the park extends far beyond the park boundaries so that<br />

activities outside the park, but within the watershed—irrigation, water diversion, <strong>and</strong><br />

introduction of pollutants—have caused ecological damage to the park, but are beyond<br />

the control of park <strong>managers</strong>. For example, fish <strong>and</strong> shrimp populations within the<br />

Everglades estuary fluctuate in response to annual patterns of freshwater inflow. Without<br />

control of this inflow, it is impossible to properly protect <strong>and</strong> manage these fishery<br />

resources. And while the park has been allocated a total freshwater inflow of<br />

430,000,000 m 3 (350,000 acre-feet) annually it has not been successful in getting the correct<br />

portions at particular critical times.<br />

a variety of hinterl<strong>and</strong> interests. The ZOI approach in the Gulf of Mannar is used to<br />

<strong>for</strong>mally negotiate cooperative management actions outside the boundaries of the<br />

official coastal reserve <strong>and</strong> which affect the reserve, such as uncontrolled fishing<br />

(Figure I-53).<br />

The ZOI approach could also work <strong>for</strong> offshore waters that extend past the<br />

statutory Coastal Zone boundary in order to cover some of the remote waters of the<br />

continental shelf (as defined by the 1982 Convention on the Law of the Sea) or the<br />

Exclusive Economic Zone (which extends to 320 km offshore) if important water use<br />

issues extend that far seaward.

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