Opportunity for regional input on investment priorities - potential GRANTS.
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 9 p
BIOPAMA inception meeting. June, 2018
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 10 p
Vision for future tools.
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 91 p
From knowledge to action for a protected planet
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 24 p
Data packs on USB sticks and printed maps
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 2 p
What is management effectiveness evaluation ?
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 57 p
Our protected area network across land and sea safeguards our precious and outstanding natural and cultural heritage. Together we manage these areas effectively for all the people of Papua New Guinea.
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 50 p
Results here represent work completed by staff at the PNG
Conservation and Environment Protection Authority (CEPA)
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 8 p
Formal Gazettal and effective management of the Torricelli Mountain Range Conservation Area -2005 to presen
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 21 p
Background of Environment Management Act.
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 140 p
Established as part of Government Initiatives e.g. Kiritimati and Southern Line Islands (1975), PIPA (2006) and Nooto Ramsar site (2013
Available online|Powerpoint presentation
Call Number: [EL]
Physical Description: 26 p
Fisheries - effects of marine protected areas on local fisheries: evidence from empirical studies.
Available online
Call Number: [EL]
Physical Description: 27 p
The impacts of house mice (Mus musculus), one of four invasive rodent species in New Zealand, are only clearly revealed on islands and fenced sanctuaries without rats and other invasive predators which suppress mouse populations, influence their behaviour, and confound their impacts. When the sole invasive mammal on islands, mice can reach high densities and influence ecosystems in similar ways to rats.
Following the incursion of rats (Rattus rattus) on Taukihepa (Big South Cape Island; 93.9 km²) off southern New Zealand in 1963, and the subsequent extirpation of several endemic species, the New Zealand Wildlife Service realised that, contrary to general belief at the time, introduced predators do not reach a natural balance with native species and that a safe breeding habitat for an increasing number of at risk species was urgently needed.
Rat eradication is a highly effective tool for conserving biodiversity, but one that requires considerable planning eff ort, a high level of precision during implementation and carries no guarantee of success. Overall, rates of success are generally high but lower for tropical islands where most biodiversity is at risk. We completed a qualitative comparative review on four successful and four unsuccessful tropical rat eradication projects to better understand the factors influencing the success of tropical rat eradications and shed light on how the risk of future failures can be minimised.
The Baja California Pacifc Islands, Mexico, are globally important breeding sites for 22 seabird species and subspecies. In the past, several populations were extirpated or reduced due to invasive mammals, human disturbance, and contaminants. Over the past two decades, we have removed invasive predators and, for the last decade, we have been implementing a Seabird Restoration Programme on eight groups of islands: Coronado, Todos Santos, San Martín, San Jerónimo, San Benito, Natividad, San Roque, and Asunción.
Considerable bene?ts can be achieved for indigenous biodiversity when invasive vertebrates are removed from islands. In New Zealand, two logistically challenging eradications were undertaken, one to remove cats (Felis catus) and the other Paci?c rats (Rattus exulans) from Te Hauturu-o-Toi/Little Barrier Island (Hauturu). Here we document the short- and long-term impacts of these interventions on the biodiversity of Hauturu. We also assess the extent to which predicted outcomes were re?ected in the measured responses for a wide range of species.
Biodiversity on marine islands is characterized by unique biogeographic. phylogenetic and functional characteristics. Island hold a disproportionate amount of the world's biodiversity, and they have also experienced a disproportionate loss of it.
Common folders - nas.sprep.org - tobedeletedonemonthlycycle - IS4Mira - Doc-To-Load - 200706_Doc to Load
Call Number: [EL]
Physical Description: 30 p.
Biodiversity tends to be at a maximum in the
equatorial region in the west of the Pacific Islands
area, and decreases markedly towards the east. For
example, the number of naturally occurring species of
animals and plants is much greater in the Solomon
Islands than in Tahiti. This is also true of the marine
environment, where fish and invertebrate species,
including corals, are far more numerous in the west
of the sub-region than in the east.
Also available electronically|2 copies
A strong state reinforces investment yield, whether this results from public or private sector investment. Th e development needs of a weak state must diff er from those of a strong state. Th e fragile states of the Pacifi c are not the dynamic societies of Asia.1 Th ese may sound like obvious statements but the special needs of Pacifi c fragile states have not been apparent in earlier approaches to development in the Pacifi c region. Current Asian Development Bank (ADB) regional and country strategies and programs diff er from those of earlier years.