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J. Seminoff, K. Shanker (2008)
Marine turtles and IUCN Red Listing: A review of the process, the pitfalls, and novel assessment approachesJournal of Experimental Marine Biology and Ecology, 356
B. Bowen, S. Karl (2007)
Population genetics and phylogeography of sea turtlesMolecular Ecology, 16
(2011)
14-15 c 2011 The Authors. Animal Conservation c 2011 The Zoological Society of London
D. Bass, P. Anderson, N. Silva (2011)
Applying thresholds to identify key biodiversity areas for marine turtles in MelanesiaAnimal Conservation, 14
B. Wallace, A. Dimatteo, Brendan Hurley, Elena Finkbeiner, A. Bolten, M. Chaloupka, B. Hutchinson, F. Abreu-Grobois, Diego Amorocho, K. Bjorndal, J. Bourjea, B. Bowen, Raquel Dueñas, P. Casale, B. Choudhury, A. Costa, P. Dutton, A. Fallabrino, Alexandre Girard, M. Girondot, M. Godfrey, M. Hamann, M. López-Mendilaharsu, M. Marcovaldi, J. Mortimer, J. Musick, R. Nel, N. Pilcher, J. Seminoff, Sebastian Tröeng, B. Witherington, R. Mast (2010)
Regional Management Units for Marine Turtles: A Novel Framework for Prioritizing Conservation and Research across Multiple ScalesPLoS ONE, 5
C. Moritz (1994)
Defining 'Evolutionarily Significant Units' for conservation.Trends in ecology & evolution, 9 10
G. Edgar, P. Langhammer, Gerry Allen, T. Brooks, J. Brodie, W. Crosse, N. Silva, L. Fishpool, Matthew Foster, D. Knox, J. Mccosker, R. Mcmanus, A. Millar, R. Mugo (2008)
Key biodiversity areas as globally significant target sites for the conservation of marine biological diversityAquatic Conservation-marine and Freshwater Ecosystems, 18
Wallace (2010)
Regional Management Units for marine turtlesa novel framework for prioritizing conservation and research across multiple scales, 5
Seminoff (2008)
Marine turtles and IUCN Red Listinga review of the process, the pitfalls, and novel assessment approaches, 356
Globally distributed, highly migratory marine megafauna present serious challenges to designing effective conservation strategies that target specific habitats and threats to population persistence. Marine turtles exhibit several characteristics that make multiple population levels, life‐history traits, and stages potentially appropriate targets for conservation ( Wallace , 2010 ), including distinct feeding and breeding areas for adults, geographically separated ontogenetic habitats, and complex population structures ( Bowen & Karl, 2007 ). Different threats that operate on various spatial scales can differentially affect the same marine turtle population, warranting distinct conservation actions. Although the International Union for the Conservation of Nature (IUCN) Red List ™ provides conservation status assessments for marine turtle species at a global level, these listings belie regional variations in population sizes and trends ( Wallace , 2010 ). This discrepancy has led the IUCN/SSC Marine Turtle Specialist Group (MTSG) to advocate for regional assessments at several scales below the species level that have been defined as biologically discrete population units ( Seminoff & Shanker, 2008 ). In a new paper, Bass, Anderson & De Silva (2011) applied the Key Biodiversity Area (KBA) approach to marine turtle nesting sites in Melanesia. As KBAs originally were developed for terrestrial
Animal Conservation – Wiley
Published: Feb 1, 2011
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