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1.3.4.2 Marine ERS ModelsDeveloping ERS models for <strong>the</strong> marine realm is often <strong>the</strong> most difficult of <strong>the</strong> threerealms due to <strong>the</strong> lack of data and <strong>the</strong> dynamic nature of <strong>the</strong> ocean, an environment that isconstantly moving. Assigning risk boundaries to <strong>the</strong> ocean is a complicated andperplexing task. Attempts to model coastal transport with ocean current data for assigningmarine risk distributions has been attempted by Schill (2005) using <strong>the</strong> cell-assignedvelocity from <strong>the</strong> Hybrid Coordinate Ocean Model (HYCOM) data model. The modeloperates using eastward and northward velocities on a cell-by-cell basis to compute atravel cost surface which represents <strong>the</strong> number of seconds it takes to cross a cell.Additional investigations are currently being conducting using <strong>the</strong> new network datamodel in ArcGIS Network Analyst.As with <strong>the</strong> o<strong>the</strong>r, ERS models,marine experts must first identify <strong>the</strong>risk elements to <strong>the</strong> marine habitats.Human activities that are riskelements can be divided into fourcategories based on <strong>the</strong>ir marineimpact: direct impacts (e.g.population density), contamination(e.g. coastal industry, ports/marinas),extraction (e.g. fishing and harvestingpractices), and watershed-basedsedimentation/run-off (land andmarine-based pollution). This processwas followed for <strong>the</strong> marine ERSmodels that were developed for <strong>the</strong>Jamaica Ecoregional PlanningMarine Analysis (Zenny, 2006).Each risk element that was identifiedand mapped by experts was assignedan intensity value, an influencedistance, <strong>the</strong>n combined to create anoverall risk surface.One idea for modeling potentialupland sedimentation on coastalenvironments is to use <strong>the</strong> flowaccumulation of <strong>the</strong> freshwater ERSmodel to gauge risk intensity atcoastal outlets. As discussed in <strong>the</strong>previous section, <strong>the</strong> flowaccumulation function aggregates androutes risk intensities to watershedoutlets, which often empty into <strong>the</strong>The creation of <strong>the</strong> Jamaican marine cost surface used in <strong>the</strong>MARXAN model included <strong>the</strong> combining of four riskcategories: contamination, direct impacts, flow accumulation,and extraction.TNC Protected Area Tools (PAT) Version 3.0The Nature Conservancy, August 200929

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