The independent island nations of the South Pacific have a rich and threatened terrestrial biota. Despite considerable investment of resources into conservation over the last three decades, biodiversity is dwindling and protected area systems remain inadequate. This lack of success is caused by important differences in cultural, economic, landownership, and social factors in developing Pacific Island countries, compared to developed nations that often fund conservation programs and plans. Despite the obvious need for capacity building and information exchange among stakeholders, little collaboration and development has eventuated. A coordinated and integrated approach, focusing conservation resources on national priorities, is essential to achieve efficient conservation. This will need to include active involvement of landowners, a good sociocultural understanding of target communities, improved collaboration between the various stakeholders, provision of sustainable alternative economic activities, and a commitment to long funding cycles for projects.

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International audiencePseudobulweria is one of the least known and most endangered of all seabird genera. It comprises six taxa, of which two are extinct, three are critically endangered and one is near threatened. Phylogenetic relationships between these taxa and position of the genus in the Order Procellariiformes have never been studied, and the taxonomic status of several taxa remains unsettled. Conservation management of Pseudobulweria taxa will be enhanced if these uncertainties are resolved. We used a multilocus gene tree approach with two mitochondrial DNA markers (cytochrome oxidase subunit 1 and cytochrome b gene) and one nuclear intron (b Fibrinogen intron 7) to investigate phylogenetic relationships within the genus using sequences from all taxa. We combined gene trees to estimate a phylogeny of the genus using a multispecies coalescent methodology. We confirmed the link between Pseudobulweria and a clade comprising Puffinus and Bulweria genera. The Fiji petrel's status, as belonging to the genus, is confirmed, as is the specific status of newly rediscovered Beck's petrel. Maintenance of the two subspecies of Tahiti petrel as currently described is not supported. Discovering the breeding grounds of all taxa is the key for their conservation, which is vital to both the marine and fragile insular tropical ecosystems where Pseudobulweria are apical predators

D a v i d O l s o n , L i n d a F a r l e y , A l e x P a t r i c k , D i c k W a t l i n g , M a r i k a T u i w a w a V i l i k e s a M a s i b a l a v u , L e m e k i L e n o a , A l i v e r e t i B o g i v a , I n g r i d Q a u q a u J a m e s A t h e r t o n , A k a n i s i C a g i n i t o b a , M o a l a T o k o t a ' a , S u n i l P r a s a d W a i s e a N a i s i l i s i l i , A l i p a t e R a i k a b u l a , K i n i k o t o M a i l a u t o k a C r a i g M o r l e y and T h o m a s A l l n u t t Abstract Fiji's National Biodiversity Strategy and Action Plan encourages refinements to conservation priorities based on analyses of new information. Here we propose a network of Priority Forests for Conservation based on a synthesis of new studies and data that have become available since legislation of the Action Plan in 2001.For selection of Priority Forests we considered minimum-area requirements for some native species, representation goals for Fiji's habitats and species assemblages, key ecological processes and the practical realities of conservation areas in Fiji. Forty Priority Forests that cover 23% of Fiji's total land area and 58% of Fiji's remaining native forest were identified. The analysis confirms the majority of conservation priority areas previously identified, recommends several new areas, and supports the Government of Fiji's policy goal of protecting 40% of remaining natural forests to achieve the goals of the National Biodiversity Strategy and Action Plan and sustain ecosystem services for Fijian communities and economies.

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