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.
PNG is endowed with rich natural resources and culture and is known as one of the cultural and mega biodiversity hotspots globally. Located on the eastern part of the island of New Guinea, PNG contains roughly 1 percent of the global landmass, with four major islands and over 600 islands and atolls. PNG also has one of the diverse reef system in the world and has a total of 3.12 square kilometers of economic exclusive zone (EEZ) of marine territory. Over 840 spoken languages exist and spoken by over 1000 different tribes.
It is desirable that all citizens of Papua New Guinea (PNG), wherever they live, have access to potable water and an appropriate standard of sewerage collection and treatment. Unfortunately, PNG‘s rugged geography makes that difficult, if not impossible, to achieve. Most of PNG‘s people live in rural areas (with over 85% of the population depending on semi-subsistence agriculture) and lack access to safe drinking water or sanitation. Apart from the cities of Port Moresby and Lae, urban areas are mostly small towns with fewer than 1,000 households.
CEPA Environment Permit Application Forms Schedule 1.
CEPA Environment Permit Application Form to Discharge Waste Schedule and Additional Information Schedule 2.
The main objective of the expedition was to compare as large a series of islands of different climatic conditions, ages and geological origins as possible. This necessitated short visits to each selected island. The structure and components of the ecosystem under study were the focus of attention, while their functioning was considered to be of secondary importance.
3 copies
Call Number: ECO [EL],PC 577.52 ECO
Physical Description: x, 220 p. : ill. ; 30 cm
In September 1991 the Government of the Marshall Islands requested assistance in compiling a bibliography of material relating to fisheries and marine resources of the Marshall Islands. After discussions between the staff of the Marshall Islands Marine Resources Authority and the Fisheries Programme of the South Pacific Commission, it was decided that a search for appropriate documents would take place in Majuro, Guam, Tokyo, Honolulu and Suva during September, October and November 1991.
Look in the SPC shelf under section I.
Call Number: 639.016 IZU
Assessments of the general condition, stocking, composition, and growth of mangroves on the islands of Pohnpei and Yap and at one area on Kosrae were undertaken at the request of these states. Methods used included: reconnaissance on foot, by air and by boat; use of 1976 aerial photographs; remeasurement of forest inventory plots installed by the US Forest Service in 1983; and installation of new inventory plots, examination of public records, and reviews of published data (Pohnpei).