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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.

,

Shwiff, Stephanie A.

,

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.
Source information for the inventory of dioxins and furan releases in the Cook Islands, September 2010
Biodiversity Conservation

Hilyard, Maureen

2010
Dioxins are organic compounds that are not produced intentionally but only as a product of other chemical procedures such as incineration, wood and fuel burning, combustion,and others. When dioxins enter the food chain,they are retained in the fatty tissue of living organisms. General hospital waste, including used bandages, are put into yellow bins to indicate that they will be burned in the incinerator. Syringes from the outer islands are delivered to the incinerator in special boxes. Needles are disposed of in a special electric burner. The incinerator area has become a dumping ground for a variety of waste not just for burning. The hospital does not have a sustainable environment policy. Quarantine wastes are incinerated at the Rarotonga airport. Two incinerators were purchased in 1973. One has only one of its two chambers operational. The other has not worked for years and has supplied parts for the other as parts are no longer available. The Airport Authority and AirNZ have had discussions about the efficiency of the incineration process, especially when food waste from LSG is included with wet waste from daily aircraft. A new incinerator for the airport is warranted if aircraft waste continues to be required to be burned at its destination.. A general survey of domestic fuel and waste burning revealed that 89% of households use gas cookers although 33%also use an umu for cooking food at least once a month. 68% burn green waste with only 2 of those who were surveyed having compost bins. 17.6 tonnes of wood and 2794 kg of LPG are burned by householders each month. Recycling is used with varying degrees of efficiency within our schools. Green waste is burned in all schools. Some attempt at composting is used in one of the primary schools. None of the schools had an environmental sustainability policy, and it was noted that students had seen already separated material combined together during the weekly collection by the waste contractors. There is not enough information about who accepts material for recycling or other more appropriate methods of disposal of school waste. In 2008,the statistics department recorded 17 million litres of gasoline and other mineral fuels imported to the Cook Islands for general use by the public for cars,boats,etc,and also by Te Aponga Uiraandthe Airport Authority. In 2010, 21% of the 9214 registered vehicles are older than 6 years with implications as to their effectiveness regarding exhaust emissions. 336,000 litres of fuel is consumed annually by the inter island shipping service and local charter and recreational craft. There is no policy about the disposal of waste oil. 11 tonnes of tobacco products including 8.5 million cigarettes were imported into the Cook Islands in 2008. 52 tonnes of plastic and polymers were imported in 2008, mainly for use by food vendors.