Mapping a Future for Southeast Asian Biodiversity

作者: Alice C. Hughes

DOI: 10.5772/33950

关键词:

摘要: Globally, biodiversity levels are currently changing at an unprecedented rate due to a myriad of anthropogenically induced factors (Sala et al., 2000). Over the next century these negative trends in set continue, and therefore identification areas for conservation prioritisation necessary order best protect greatest diversity (Brook 2006). Though studies have used different criteria areas, some combined number (Myers 2000) which led 25 global hotspots species endemicity, only comprise 1.4% land surface, but contain 44% all known plant 35% described vertebrates.

参考文章(127)
S. Hedges, J. W. Duckworth, Bird records from Cambodia in 1997, including records of sixteen species new for the country Forktail. ,vol. 1, pp. 29- 36 ,(1998)
Waranoot Tungittiplakorn, Philip Dearden, Biodiversity conservation and cash crop development in northern Thailand Biodiversity and Conservation. ,vol. 11, pp. 2007- 2025 ,(2002) , 10.1023/A:1020812316749
Philip Gibbons, David Lindenmayer, Tree Hollows and Wildlife Conservation in Australia Tree hollows and wildlife conservation in Australia.. ,(2002) , 10.1071/9780643090033
Vincent Carignan, Marc-André Villard, Selecting indicator species to monitor ecological integrity: a review. Environmental Monitoring and Assessment. ,vol. 78, pp. 45- 61 ,(2002) , 10.1023/A:1016136723584
Jayasilan Mohd-Azlan, Akbar Zubaid, Thomas H Kunz, None, Distribution, relative abundance, and conservation status of the large flying fox, Pteropus vampyrus, in peninsular Malaysia: A preliminary assessment Acta Chiropterologica. ,vol. 3, pp. 149- 162 ,(2001)
Martin T. Sykes, Wolfgang Cramer, I. Colin Prentice, A bioclimatic model for the potential distributions of North European tree species under present and future climates Journal of Biogeography. ,vol. 23, pp. 203- 233 ,(1996) , 10.1046/J.1365-2699.1996.D01-221.X