In particular, in paragraph 178, Member States reiterate the condition of SIDS as "a special case for sustainable development in view of their unique and particular vulnerabilities, including their small size, remoteness, narrow resource and export base, and exposure to global environmental challenges and external economic shocks, including to a large range of impacts from climate change and potentially more frequent and intense natural disasters". The SIDS Partnership Framework also encourages national and regional partnership dialogues to be organized through existing forums and meetings. ĝESA to finalize a standardized partnership reporting template and process of SIDS partnerships.Organization on an annual basis a Global Multi-stakeholder SIDS Partnership Dialogue.Steering Committee - open to all States Members of the United Nations or members of the specialized agencies, chaired by one small island developing State and one State that is not a small island developing State, to be appointed by the President of the General Assembly.The SIDS Partnership Framework consists of:
#Island racer 2018 pdf full#
The SIDS Partnership Framework, which is to monitor and ensure the full implementation SIDS partnerships, is based on a set of recommendations which were prepared by DSD in close consultation with member States. We suggest conservation actions such as invasive species management and habitat restoration to enable further recovery.On 4 December 2015 the 2nd Committee adopted the draft resolution (A/C.2/70/L.47) which decided to establish the Small Island Developing States Partnership (SIDS) Framework, in accordance with paragraph 101 of the SAMOA Pathway. Given the current small size of the remaining population and the presence of invasive species across the snake’s range, this species could be at risk of local extirpation. The decrease in encounter rates between 20 implies a negative impact of the hurricanes on racer abundance. The pre-hurricane encounter rate of individual racers was 16.0 snakes/hour compared to 0.34 snakes/hour in 2018 and 0.41 snakes/hour in 2019 (post-hurricane).
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Surveys were conducted at seven sites in 2011 prior to the hurricanes, and at 81 and 108 sites in 20 respectively posterior to the hurricanes. Eustatius in 2011, 20 to determine the likely influence of hurricanes Irma and Maria (September 2017), in addition to evaluating abiotic parameters which may be correlated with its presence. We estimated population densities of the red-bellied racer (Alsophis rufiventris) on the Caribbean island of St. Despite this, given the species’ extremely limited extant range and the presence of invasive species on both islands, prevention of local extirpation should be a high conservation priority. Nevertheless, our results suggest that racer densities on Saba are currently higher than those on St. Using Distance sampling, we estimated 10.9 (min 7.3, max 16.2) racers/ha, with a total population estimate of 4,917 (min 2,577, max 6,362) across the entire study region (438.6 ha.) Based on anecdotal observations from Saban residents and prior literature describing the pre-hurricane population as “abundant” (at least 2.0 racers/hour), we posit that the population experienced a hurricane-induced decline but may have since recovered, though not to previous levels (1.28 racers/hour).
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Detection probability was estimated at 0.15 (min 0.10, max 0.21). Similarly, lambda was estimated at 1.61 (min 0.7, max 3.7) but varied between vegetation types and elevational gradients.
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The proportion of sites occupied was estimated at 0.74 (min 0.48, max 0.90), with occupancy varying between vegetation types and across elevational gradients. Line transect surveys were conducted at 74 sites covering 6.7 ha. We estimated occupancy, abundance (lambda), detection probability, density/ha and abundance of a regionally endemic snake in the Colubrid family on the Dutch Caribbean island of Saba in 2021, four years after hurricanes Irma and Maria impacted the island.