1 1.10 Application of estuarine and coastal classifications in marine ...
1 1.10 Application of estuarine and coastal classifications in marine ...
1 1.10 Application of estuarine and coastal classifications in marine ...
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<strong>and</strong> cottages, <strong>and</strong> tourism related companies. This <strong>in</strong>formation is useful <strong>in</strong> assess<strong>in</strong>g the impact<br />
<strong>of</strong> different zon<strong>in</strong>g scenarios on the mar<strong>in</strong>e <strong>and</strong> <strong>coastal</strong> tourism associated economy. For<br />
example, if a zon<strong>in</strong>g regulation prohibits development <strong>of</strong> docks, hotels or boat<strong>in</strong>g then the cost<br />
can be calculated for specific regions. Furthermore, the <strong>in</strong>formation can be comb<strong>in</strong>ed to show the<br />
overall picture <strong>of</strong> the economy geographically<br />
<strong>1.10</strong>.11.1 Classify<strong>in</strong>g <strong>and</strong> Mapp<strong>in</strong>g Ecosystem Services<br />
Ecosystem services are the benefits people obta<strong>in</strong> either directly or <strong>in</strong>directly from<br />
ecological systems (Millenium Ecosystem Assessment 2003) <strong>and</strong> are a critical component <strong>of</strong><br />
comprehensive mar<strong>in</strong>e spatial plann<strong>in</strong>g. An ecosystems services approach to valu<strong>in</strong>g mar<strong>in</strong>e<br />
biodiversity is recognized as a framework by which economic, ecological <strong>and</strong> social values can<br />
be <strong>in</strong>corporated <strong>in</strong>to the decision mak<strong>in</strong>g process (Rees et al. 2010) <strong>and</strong> <strong>in</strong>clusion can help to<br />
promote efficient strategies for biodiversity conservation <strong>and</strong> anticipate stakeholder conflicts<br />
(Beaumont et al. 2007). Naidoo et al. (2008) argued that to underst<strong>and</strong> the <strong>in</strong>teraction between<br />
biodiversity <strong>and</strong> ecosystem services, values must be quantified <strong>and</strong> their areas <strong>of</strong> production<br />
mapped. An <strong>in</strong>creas<strong>in</strong>g amount <strong>of</strong> spatially-explicit <strong>in</strong>formation is be<strong>in</strong>g collected on the<br />
ecological <strong>and</strong> socio-economic value <strong>of</strong> goods <strong>and</strong> services associated with <strong>coastal</strong> ecosystems<br />
(Chan et al. 2006). De Groot et al. (2002) def<strong>in</strong>ed 23 ecosystem functions with a wide range <strong>of</strong><br />
examples <strong>of</strong> goods <strong>and</strong> services provided by these functions that can be classified <strong>in</strong>to three<br />
groups: 1.) ecological, 2.) socio-cultural, <strong>and</strong> 3.) economic value. Troy <strong>and</strong> Wilson (2006)<br />
developed a spatial framework for the analysis <strong>of</strong> ecosystem service values (ESVs) through<br />
<strong>in</strong>tegration <strong>of</strong> biophysical l<strong>and</strong> use units classified from remotely sensed data with estimates <strong>of</strong><br />
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