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A guide for planners and managers - IUCN

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PART I<br />

Strategies <strong>and</strong> Tools<br />

Habitat Classification: In order to produce digital marine ecosystem maps, a<br />

marine habitat classification scheme must exist. Such a scheme should have biological<br />

<strong>and</strong> physical parameters <strong>for</strong> the ecosystem. The scheme should be hierarchical <strong>and</strong><br />

nest highly detailed habitat descriptions into more generalized habitat descriptions.<br />

The scheme should provide sufficient detail <strong>for</strong> research, conservation, <strong>and</strong> management<br />

needs. Finally, the scheme should recognize the limitations of the remote sensing<br />

technology to discriminate features in the marine environment. An accurate, highresolution<br />

shoreline is the base map upon which all other map layers are superimposed.<br />

Shoreline links terrestrial ecosystems to marine ecosystems. In addition, datum<br />

adjustments must be applied to the shoreline to properly place this key feature on<br />

the earth. Ef<strong>for</strong>ts must continue to develop accurate, high-resolution, datum-corrected<br />

digital shoreline maps.<br />

Bathymetry: This is a critical thematic data layer <strong>for</strong> many mapping activities.<br />

Bathymetry depicting water depths of less than 100 m is needed to identify <strong>and</strong><br />

locate navigation hazards <strong>and</strong> shipping channels, predict <strong>and</strong> manage the damage<br />

from floods <strong>and</strong> storms, identify <strong>and</strong> monitor critical fish habitat, <strong>and</strong> document the<br />

location <strong>and</strong> extent of shallow coral reef ecosystems. Bathymetry also is required to<br />

fully utilize remotely sensed data to correct <strong>for</strong> light attenuation. Light received by<br />

the sensor is affected by the distance that it must travel through the water column.<br />

Fortunately, most corals are found in shallow-water environments of less than 30 m.<br />

Remote Sensing Costs: Data acquisition accounts <strong>for</strong> about 25 percent of the<br />

total cost of producing marine ecosystem maps. The remaining 75 percent goes to<br />

georeferencing the imagery, calibrating the imagery, validating the draft maps, <strong>and</strong><br />

producing the final map products.<br />

Airborne LIDAR costs range from US$900 to 1,800 per sq km depending upon<br />

the horizontal spatial resolution needed. Deep water (> 50 m) bathymetry also is crucial<br />

<strong>for</strong> many mapping activities, including coral reef ecosystem mapping. Ship-based<br />

acoustic surveys using multibeam depth sounders have successfully produced<br />

bathymetric maps with vertical accuracies of +/- 15 cm from depths 10 m to 500 m<br />

<strong>and</strong> greater. In addition to providing highly accurate bathymetric maps, the system<br />

provides backscatter, which can be used to map the roughness of the seafloor. Costs<br />

of multibeam range from US$1,000 to 4,000 per sq. km depending on the type of boat<br />

required. When assessing airborne remote sensing technology, the cost is most<br />

affected by the altitude flown <strong>and</strong> the "footprint" of the resulting imagery. Typically,<br />

aerial photography costs about US$125/sq. km.<br />

Due to their large footprint, satellite imagery costs range from $100/sq. km. <strong>for</strong><br />

IKONOS to $6/sq. km. <strong>for</strong> L<strong>and</strong>Sat 7.<br />

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