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A guide for planners and managers - IUCN

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PART II<br />

Protected Areas <strong>for</strong> Lagoons <strong>and</strong> Estuaries<br />

You can enter on the base map—manually or electronically—known critical<br />

habitats of species both inside <strong>and</strong> outside the estuary, including submerged sea<br />

grass <strong>and</strong> algal beds, as well as connections to the sea (lagoon mouths, deltaic<br />

channels). Some critical habitats may overlap others, <strong>for</strong> example the nesting <strong>and</strong><br />

roosting sites of shorebirds <strong>and</strong> seabirds in mangroves may overlap the habitat of<br />

muskrats in marshes (Figure II-21). Designated habitats should include those of<br />

commercial species, showcase species, <strong>and</strong> endangered species.<br />

Highlight the selected critical habitats<br />

--whether using manual methods of mapping<br />

or GIS—<strong>and</strong> indicate the recommended<br />

management approach <strong>for</strong> each on the map.<br />

Be aware that the areas chosen may be<br />

subject to multiple use, not exclusively<br />

assigned to protection, <strong>and</strong> the recommended<br />

extent of such uses has to be clearly indicated<br />

so that zones can be designated.<br />

You will need to investigate the pattern<br />

of human use <strong>and</strong> settlement in the estuary<br />

<strong>and</strong> record significant sources of impacts. In<br />

larger inhabited estuaries where there has<br />

been some use <strong>and</strong> alteration of wetl<strong>and</strong>s <strong>and</strong><br />

other coastal habitats, identify the remaining areas of high conservation value, which<br />

generally will be those in a natural state, removed from human settlements, or<br />

currently managed <strong>for</strong> recreation, research or education, or as private nature reserves.<br />

Depending on the extent <strong>and</strong> location of settlement <strong>and</strong> commercial use, a larger<br />

estuary can be zoned <strong>for</strong> different MPA management approaches, or as mentioned<br />

above, allotted to CZM protection if there is an effective CZM process <strong>for</strong> the lagoon<br />

or estuary. In this case, the most valuable <strong>and</strong> vulnerable critical habitats should be<br />

given the fullest protection that MPAs can af<strong>for</strong>d through zoning or other means.<br />

2.7 Delineating the Zone of Influence<br />

FIGURE II-21.<br />

A muskrat house on a transitional brackish tidal<br />

marsh next to a small creek (Pautuxent River,<br />

Chesapeake Bay, Maryl<strong>and</strong>, U.S.A.).<br />

Water supply is vital to the estuary’s functioning. Sources of water include the<br />

catchment, rivers <strong>and</strong> streams crossing the watershed, groundwater seepage <strong>and</strong><br />

sheet flow (runoff), rainfall, <strong>and</strong> intrusion of salt water from the sea. These water sources<br />

link estuaries to agricultural <strong>and</strong> development activities that are tens, even hundreds,<br />

of kilometers away. Disturbance of these sources--including their reduction, diversion,<br />

<strong>and</strong> pollution—may have disastrous consequences <strong>for</strong> estuarine ecosystems. Such<br />

distant activities are difficult to monitor, but must be controlled if an estuary <strong>and</strong> its<br />

valuable components are to survive. When the main catchments that discharge to the<br />

estuary lie close at h<strong>and</strong> <strong>and</strong> are not heavily settled, the two may be protected as single<br />

“source-to- sink” units.<br />

201<br />

Photo by John Clark.

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