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Dispersal connectivity and reserve selection for marine conservation
Authors:Stuart Kininmonth  Maria BegerMichael Bode  Eric PetersonVanessa M. Adams  Dan DorfmanDaniel R. Brumbaugh  Hugh P. Possingham
Affiliation:a Australian Institute of Marine Science, PMB #3, Townsville MC, Queensland 4810, Australia
b The University of Queensland, School of Biological Sciences, The Ecology Centre and Commonwealth Research Facility for Applied Environmental Decision Analysis, Brisbane, QLD 4072, Australia
c University of Melbourne, The Applied Environmental Decision Analysis Group, School of Botany, Melbourne 3010, Victoria, Australia
d University of the Sunshine Coast, Sippy Downs, Queensland, Australia
e Australian Research Council Centre of Excellence for Coral Reef Studies, James Cook University, Townsville Qld 4811, Australia
f NOAA/NOS/NCCOS/CCMA/Biogeography Branch, 1305 East West Highway, SSMC4 Rm 9320, Silver Spring, MD 20910, USA
g Center for Biodiversity and Conservation, American Museum of Natural History, New York, NY 10024, USA
Abstract:Although larval dispersal is crucial for the persistence of most marine populations, dispersal connectivity between sites is rarely considered in designing marine protected area networks. In particular the role of structural characteristics (known as topology) for the network of larval dispersal routes in the conservation of metapopulations has not been addressed. To determine reserve site configurations that provide highest persistence values with respect to their connectivity characteristics, we model nine connectivity topological models derived from graph theory in a demographic metapopulation model. We identify reserve site configurations that provide the highest persistence values for each of the metapopulation connectivity models. Except for the minimally connected and fully connected populations, we observed two general ‘rules of thumb’ for optimising the mean life time for all topological models: firstly place the majority of reserves, so that they are neighbours of each other, on the sites where the number of connections between the populations is highest (hub), secondly when the reserves have occupied the majority of the vertices in the hub, then select another area of high connectivity and repeat. If there are no suitable hubs remaining then distribute the remaining reserves to isolated locations optimising contact with non-reserved sites.
Keywords:Marine larvae dispersal   Marine conservation planning   Marine reserves   Connectivity   Marine metapopulation model
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