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A guide for planners and managers - IUCN

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2.8 General In<strong>for</strong>mation Needs<br />

PART II<br />

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

Planning <strong>for</strong> MPAs in estuaries or lagoons requires detailed ecological knowledge. The<br />

protected area manager should have a thorough knowledge of the physical, chemical,<br />

<strong>and</strong> biological parameters of the estuarine ecosystem <strong>and</strong> when possible participate<br />

in research in the field (see Boxes II-2 <strong>and</strong> II-3). Research <strong>and</strong> monitoring studies <strong>and</strong><br />

periodic management plan revisions are the basis <strong>for</strong> the most successful management<br />

of lagoons <strong>and</strong> estuaries. But only occasionally has sufficiently detailed research<br />

preceded protected area design.<br />

Box II-2. Physical In<strong>for</strong>mation <strong>for</strong> Lagoon <strong>and</strong> Estuary MPAs.<br />

Geomorphology of a basin reveals a wealth of in<strong>for</strong>mation on the likely functions<br />

<strong>and</strong> characteristics of the ecosystem. Classifying the estuary by type requires little more<br />

than visual inspection.<br />

Bottom topography can yield features of ecological significance (shape of bottom<br />

affects currents; shallow areas have higher photosynthetic rates, etc.). Depths can be taken<br />

by a cheap electronic meter or simple lead line.<br />

Bottom types reveal biological activity types that are particularly diagnostic <strong>for</strong><br />

estuaries. Samples of bottom sediments are easily obtained by simple methods; a bamboo<br />

tube would be sufficient in many cases to distinguish among s<strong>and</strong>, mud, gravel, <strong>and</strong> ooze.<br />

Salinity gradient (seasonal <strong>and</strong> sporadic) is easily determined with a direct reading<br />

salinometer (see Chemical in Box X), although “presence or absence” can be learned from<br />

the “taste test.”<br />

Tidal flux in most estuaries is a dominant hydrological <strong>for</strong>ce. Measure diurnal<br />

changes by use of water level gauges (marked stick), tidal velocities (movement of a float)<br />

<strong>and</strong> extent of substrate exposed <strong>and</strong> flooded. Tide tables are usually available <strong>for</strong> navigable<br />

estuaries.<br />

Current patterns influence the degree of mixing between seawater <strong>and</strong> sedimentation.<br />

Currents may be powered by tides, external marine currents, rivers, <strong>and</strong> wind. Surface<br />

currents can be plotted with floating objects, like bottles or coconut husks.<br />

Turbidity results from suspended particles of silt, organic detritus, <strong>and</strong> plankton.<br />

It influences light penetration <strong>and</strong> photosynthesis. Turbidity can be measured with a Secchi<br />

disc (a white-<strong>and</strong>-black painted, weighted disc lowered from the surface by cord).<br />

Geomorphological dynamics indicate stability of different substrates in the basin<br />

which may be shifting or filling. An outlet may silt up or a s<strong>and</strong>bar <strong>for</strong>m or a new outlet<br />

may open, seasonally, over a few years or overnight during storms. The MPA manager<br />

can monitor these dynamics using trees, buildings, etc as visual benchmarks, or stakes<br />

driven into the ground. More sophisticated survey techniques (remote sensing) may also<br />

be used.<br />

Seasonal considerations, including rainfall, air <strong>and</strong> water temperatures, insulation<br />

(sunshine), tides, <strong>and</strong> hydrology are all important.<br />

Source: Carr, 1982b.<br />

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