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Extinction dynamics under extreme conservation threat: The flora of St. Helena Cronk, Quentin; Lambdon, Phil

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Abstract The flora of the island of St Helena provides an amplified system for the study of extinction by reason of the island’s high endemism, small size, vulnerable biota, length of time of severe disturbance (since 1502), and severity of threats. Endemic plants have been eliminated from 96.5% of St Helena by habitat loss. There have been eight recorded extinctions in the vascular flora since 1771 giving an extinction rate of 581 extinctions per million species per year (E/MSY). This is considerably higher than background extinction rates, variously estimated at 1 or 0.1 E/MSY. We have no information for plant extinctions prior to 1771 but applying the same extinction rate to the period 1502 to 1771 suggests that there may be around ten unrecorded historical extinctions. We use census data and population decline estimates to project likely extinction forward in time. The projected overall extinction rate for the next 200 years is somewhat higher at 625 E/MSY. However, our data predict an extinction crunch in the next 50 years with 4 species out of the remaining 48 likely to become extinct during this period. It is interesting that during a period when the native plant areas dropped to 3.5% of the original, the extinction rate appears to have remained shallowly linear with under 30% of the endemic flora becoming extinct.; Methods The time to percent decline (TPD) figures (see above) were standardized by conversion to half-lives (time to 50% decline: TPD50) using a simple exponential function, i.e. t1/2=t/log1/2(Nt/N0), where t1/2is the half-life (TPD50), t is the time period over which population decline has been measured, and Nt/N0is the proportion of the population remaining after t. We use the exponential for the decline curves as this is a very common general form of decline curve (Di Fonzo et al., 2013). The TPD50 for a species is therefore assumed to be constant, following an exponential decay process. The TPD50 was then used in combination with the total number of mature individuals (NMI) to project changes in NMI forward in time. Under this simple model, plants are taken as extinct when NMI <1.

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Title	Extinction dynamics under extreme conservation threat: The flora of St. Helena
Creator	Cronk, Quentin; Lambdon, Phil
Date Issued	2021-05-19
Description	<b>Abstract</b><br/><p style="text-align:start;text-indent:0px;"><span style="font-style:normal;"><span style="font-weight:normal;"><span style="letter-spacing:normal;"><span style="white-space:normal;">The flora of the island of St Helena provides an amplified system for the study of extinction by reason of the island’s high endemism, small size, vulnerable biota, length of time of severe disturbance (since 1502), and severity of threats. Endemic plants have been eliminated from 96.5% of St Helena by habitat loss. There have been eight recorded extinctions in the vascular flora since 1771 giving an extinction rate of 581 extinctions per million species per year (E/MSY). This is considerably higher than background extinction rates, variously estimated at 1 or 0.1 E/MSY. We have no information for plant extinctions prior to 1771 but applying the same extinction rate to the period 1502 to 1771 suggests that there may be around ten unrecorded historical extinctions. We use census data and population decline estimates to project likely extinction forward in time. The projected overall extinction rate for the next 200 years is somewhat higher at 625 E/MSY. However, our data predict an extinction crunch in the next 50 years with 4 species out of the remaining 48 likely to become extinct during this period. It is interesting that during a period when the native plant areas dropped to 3.5% of the original, the extinction rate appears to have remained shallowly linear with under 30% of the endemic flora becoming extinct.</span></span></span></span></p>; <b>Methods</b><br /><p style="text-align:start;text-indent:0px;"><span style="font-style:normal;"><span style="font-weight:normal;"><span style="letter-spacing:normal;"><span style="white-space:normal;">The time to percent decline (TPD) figures (see above) were standardized by conversion to half-lives (time to 50% decline: TPD50) using a simple exponential function, i.e. t<sub>1/2</sub>=t/log<sub>1/2</sub>(N<sub>t</sub>/N<sub>0</sub>), where t<sub>1/2</sub>is the half-life (TPD50), t is the time period over which population decline has been measured, and N<sub>t</sub>/N<sub>0</sub>is the proportion of the population remaining after t. We use the exponential for the decline curves as this is a very common general form of decline curve (Di Fonzo et al., 2013). The TPD50 for a species is therefore assumed to be constant, following an exponential decay process. The TPD50 was then used in combination with the total number of mature individuals (NMI) to project changes in NMI forward in time. Under this simple model, plants are taken as extinct when NMI <1.</span></span></span></span></p>
Subject	Other; plant extinction; extinction rate; oceanic island; island extinction; St Helena; dark extinction; Extinction debt; species-area curve
Type	Dataset
Notes	Dryad version number: 6</p> Version status: submitted</p> Dryad curation status: Published</p> Sharing link: http://datadryad.org/stash/dataset/doi:10.5061/dryad.sbcc2fr32</p> Storage size: 204134</p> Visibility: public</p>
Date Available	2024-07-31
Provider	University of British Columbia Library
License	CC0 1.0
DOI	10.14288/1.0397534
URI	https://doi.org/10.5683/SP2/2JRARQ
Publisher DOI	https://doi.org/10.5683/SP2/2JRARQ; https://doi.org/10.5061/dryad.sbcc2fr32
Grant Funding Agency	Natural Sciences and Engineering Research Council
Rights URI	http://creativecommons.org/publicdomain/zero/1.0
Aggregated Source Repository	Dataverse

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