Given the conservative coverage area targets, clear thought must be given to maximizing the impact of each unit of ocean area protected. We emphasize that it is not the size of individual sanctuaries that is the most important matter, but rather the global scale of coverage (Guenétte, et. al. 2003). There are several general principles that should be followed when selecting locations for marine reserves. To properly function as a buffer against external exploitation, the 10% of ocean area must include a representative sample of habitats and ecosystems should be protected (Ballantine 1991). Particular emphasis should be placed on protecting especially fragile, unique, or threatened ecosystems. Furthermore, multiple examples of each habitat type should be protected to insure against localized disturbances. Finally, individual Marine Reserves should be set up in mutually reinforcing networks to maximize there influence. Such systems rely on knowledge of the physical processes in play in a given area, especially the activity of advective and convective current systems (Johnson, Funicelli, & Bohnsack 1999 and Ballantine 1991).
Although the No-Take Zones in this proposal are intended to primarily target entire ecosystems, we acknowledge that there are biological or economic situations in which a certain organism is of particular importance. In such cases, an understanding of the relevant biology and ecology is critically important. For example, key life stages or migration routes of the target species can be protected by careful placement of reserves (Robichaud & Rose 2004). A land-based analogy is the protection of bird nesting sites and reserves for migratory birds, respectively. When setting up marine reserves, it is also important to consider potential ecological barriers that will prevent the occurrence of spillover, and therefore reduce the ability of the protected area to enhance adjacent fisheries. For instance, one study in the Turks and Caicos Islands found that numerous shallow sand habitats enclosed a population of conch, reducing its spillover into nearby areas (A. Tewfik and C. Bene, 2003).
Of course, there are also the practical matters of cost and enforceability that must be factored into any setup of marine protected areas. Creating a layout for Marine reserves that optimizes these numerous biological, physical, and social factors is a complex issue. Fortunately, there exist several environmental modeling packages such as Marxan (Possingham, Ball, & Andleman 2000), ResNet, and C-Plan that use stochastic statistical methods to optimize these parameters. Naturally, these types of algorithms are effective only given proper data, so continued emphasis on the collection of scientific data is essential. (Hyperlink to EXTERNAL FURTHER RESEARCH PAGE).