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A guide for planners and managers - IUCN

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198 MARINE AND COASTAL<br />

PROTECTED AREAS<br />

2.5 Design of the Marine Protected Area<br />

Regardless of how small or how large the portion of the lagoon or estuary that is<br />

intended <strong>for</strong> an MPA, it is necessary to address the entire estuarine ecosystem. When<br />

you cannot designate a whole estuary as an MPA, we suggest using one of the<br />

techniques mentioned above <strong>and</strong> either 1) attempt to invoke CZM <strong>for</strong> the whole<br />

estuary, or 2) attempt to set up a ZOI coordinating entity.<br />

The policy of the planner should be to design the protected area following<br />

procedures like those described herein. First a strategy should be worked out <strong>and</strong> a<br />

Strategic Plan created. Second a Site Management Plan should be created with<br />

specific mechanisms <strong>for</strong> periodic review <strong>and</strong> any needed revisions of design based<br />

on new management studies. Assuming no initial expert assistance <strong>and</strong> little knowledge<br />

of the life histories of estuary-dependent species, the protected area should be<br />

designed to encompass as many habitats as possible.<br />

The actual design work should follow the procedure in the earlier chapter on<br />

site planning (Section I-2). The objective is to design the lagoon or estuarine protected<br />

area around its principal habitats as revealed by field surveys of flora <strong>and</strong> fauna. The<br />

number of zones, if any, <strong>and</strong> the size of the protected area will depend on management<br />

objectives, examples of which are listed in Table II-12. Conserving estuary-dependent<br />

commercial species may require protecting a range of critical habitats both inside<br />

<strong>and</strong> outside the estuary.<br />

2.6 Identifying Critical Habitats<br />

Managing an estuary requires protecting the critical habitats of estuary-dependent<br />

species. The identification of these sites <strong>and</strong> processes requires knowing the geographic<br />

biology, particularly the life histories of key estuarine organisms. Each species has a<br />

characteristic requirement including substrate type, water depth, water clarity,<br />

dissolved oxygen content, <strong>and</strong> type of habitat (e.g., mangrove prop roots, marsh<br />

grass, or sea grass stems). And each key species has critical habitats that it uses during<br />

its life cycle. Such critical habitats are numerous <strong>and</strong> diverse (Box II-1).<br />

Many habitats, per<strong>for</strong>m special nurturing functions <strong>for</strong> certain species, including<br />

low intertidal marshes, high marsh tide pools, mangrove swamps, swamp <strong>and</strong> marsh<br />

creeks, mud <strong>and</strong> s<strong>and</strong> flats, passes or openings to the open ocean, open beaches, sea<br />

grass beds, macroalgae beds, rocky shores <strong>and</strong> tide pools, <strong>and</strong> many types of coral<br />

reefs, from patch reefs to extensive barrier reefs.<br />

If the MPA is nested within a CZM area, special habitats may be identified <strong>for</strong><br />

different categories of management, not just MPA management. Examples of three<br />

such categories previously discussed in Section II-5.8 are: 1. Generic habitat types; 2.<br />

Specific sites (critical areas); <strong>and</strong> 3. MPAs.

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