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  • Material Type Article
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  • Publication Year 2010
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Potential economic damage from introduction of Brown Tree Snakes, Boiga Irregularis (Reptilia: Colubridae), to the Islands of Hawaii
BRB

Gebhardt, Karen

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Kirkpatrick, Katy N.

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Shwiff, Stephanie A.

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Shwiff, Steven S.

2010
The Brown Tree Snake (Boiga irregularis) has caused ecological and economic damage to Guam, and the snake has the potential to colonize other islands in the Paci c Ocean. This study quanti es the potential economic damage if the snake were translocated, established in the state of Hawai‘i, and causing damage at levels similar to those on Guam. Damages modeled included costs of medical treatments due to snakebites, snake-caused power outages, and decreased tourism resulting from effects of the snake. Damage caused by presence of the Brown Tree Snake on Guam was used as a guide to estimate potential economic damage to Hawai‘i from both medical- and power outage–related damage. To predict tourism impact, a survey was administered to Hawaiian tourists that identi ed tourist responses to potential effects of the Brown Tree Snake. These results were then used in an input-output model to predict damage to the state economy. Summing these damages resulted in an estimated total potential annual damage to Hawai‘i of between $593 million and $2.14 billion. This economic analysis provides a range of potential damages that policy makers can use in evaluation of future prevention and control programs.
The use of Starlicide in preliminary trials to control invasive common myna Acridotheres tristis populations on St Helena and Ascension islands, Atlantic Ocean

Feare, Chris J.

2010
Introduced common mynas Acridotheres tristis have been implicated as a threat to native biodiversity on the oceanic islands of St Helena and Ascension (UK). A rice-based bait treated with Starlicide® was broadcast for consumption by flocks of common mynas at the government rubbish tips on the two islands during investigations of potential myna management techniques. Bait was laid on St Helena during two 3-day periods in July and August 2009, and on Ascension over one 3-day period in November 2009. As a consequence of bait ingestion, dead mynas were found, especially under night roosts and also at the main drinking area on Ascension, following baiting. On St Helena early morning counts at the tip suggested that whilst the number of mynas fell after each treatment, lower numbers were not sustained; no reduction in numbers flying to the main roost used by birds using the tip as a feeding area was detected post-treatment. On Ascension, the number of mynas that fed at the tip and using a drinking site, and the numbers counted flying into night roosts from the direction of the tip, both indicated declines of about 70% (from about 360 to 109 individuals). Most dead birds were found following the first day of bait application, with few apparently dying after baiting on days 2 and 3. Despite the low concentration of Starlicide used, aversion to the bait was apparent during the trials. These results indicate that Starlicide may contribute to myna control programmes but questions remain over the mode of action of the chemical (in terms of individual differences among birds the responses to its toxic properties) and the longer-term susceptibility of birds to baiting.
Warming Seas in the Coral Triangle: Coral Reef Vulnerability and Management Implications

Bruno, John F.

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Casey, Kenneth S.

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McLeod, Elizabeth

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Menviel, Laurie

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Moffitt, Russell

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Palmer, Michael J.

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Salm, Rodney

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Selig, Elizabeth R.

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Timmermann, Axel

2010
The highest diversity coral reefs in the world, located in the Coral Triangle, are threatened by a variety of local stresses including pollution, overfishing, and destructive fishing in addition to climate change impacts, such as increasing sea surface temperatures (SSTs), and ocean acidification. As climate change impacts increase, coral reef vulnerability at the ecoregional scale will have an increasingly important influence on conservation management decisions. This project provides the first detailed assessment of past and future climatic stress, thermal variability, and anthropogenic impacts in the Coral Triangle at the ecoregional level, thus incorporating both local (eg. pollution, development, and overfishing) and global threats (increasing SSTs). The development of marine protected area (MPA) networks across the Coral Triangle is critical for the region to address these threats. Specific management recommendations are defined for MPA networks based on the levels of vulnerability to the therma stress may be priorities for establishment of MPA networks, wheras high vulnerability regions may require selection and design principles aimed at building resilience to climate change. The identification of climate and other human threats to coral reef systems and ecoregions can help conservation practitioners prioritize management responses to address these threats and identify gaps in MPA networks or other management mechanisms (eg. integrated coastal management).