|Scientific Name:||Dendroica angelae|
|Species Authority:||Kepler & Parkes, 1972|
|Red List Category & Criteria:||Vulnerable D2 ver 3.1|
|Reviewer/s:||Butchart, S. & Symes, A.|
|Contributor/s:||Rodriguez, R., Anadón, V., Delannoy, C. & Colón-Merced, R.|
|Facilitator/s:||Isherwood, I., Mahood, S., Pople, R., Sharpe, C J, Wege, D.|
This species is listed as Vulnerable because it has a very small range and, were data to show that it is declining in population or range, it would be uplisted to Endangered.
|Range Description:||Dendroica angelae was only discovered in 1968 and is endemic to Puerto Rico (to USA) (Raffaele 1983). It was formerly considered to occur at four disjunct localities: in the east, the Sierra de Luquillo (El Yunque National Forest/Bosque Nacional del Caribe) and the Sierra de Cayey (Carite State Forest) and, in the west, the Cordillera Central (Maricao and Toro Negro Commonwealth Forests), but its existence at some of these sites has been questioned and it is now thought to be restricted to two widely separated locations: the Sierra de Luquillo and Maricao State Forest (Anadon-Irizarry 2006, Delannoy 2006). In optimal habitat it can be locally common, and although the population was previously thought to be no more than c.300 pairs (Curson et al. 1994), more accurate counts put the population at 1,830 individuals.|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The population is estimated to number at least 1,800 mature individuals, based on censuses conducted using playback methods. This is roughly equivalent to at least 2,700 individuals in total.|
|Habitat and Ecology:||Although it inhabits elfin or montane dwarf forest on ridges and summits, montane wet forest, and sometimes ranges to lower-elevation wet forest, it reaches its highest densities in Podocarpus dominated forest (Cruz and Delannoy 1984, Raffaele et al. 1998, Delannoy 2006). Preferred areas have a dense canopy with vines, high subcanopy and sparse understorey (Curson et al. 1994, Raffaele et al. 1998). It shows a string preference for undisturbed forest, but has been recorded in secondary habitats and plantations (Cruz and Delannoy 1984). Breeding takes place in March-June, and the nest is built in aerial leaf-litter trapped in vegetation or vines, usually close to the trunk, or in a tree cavity (Curson et al. 1994, Raffaele et al. 1998, Rodriguez-Mojica 2004).|
|Major Threat(s):||By the late 1940s, the natural vegetation of Puerto Rico had been reduced to c.6% of the island's land surface, but rapid regeneration of forest increased this figure to 31% in the early 1980s, a change which will probably benefit this species (Cruz and Delannoy 1984). However, Podocarpus dominated forest, which may be crucial to this species survival, makes up a tiny percentage of the total remaining forest and continues to destroyed by infrastructure projects, including tourism developments in protected areas (R. Rodriguez in litt. 2007). Natural disasters will continue to be a threat while the species's population and range remain so small.|
Conservation Actions Underway
Ensure the complete protection of the two sites where it persists. Assess the current distribution (especially by surveying away from known sites) and population. Research factors limiting range and population, and attempt to determine why it disappeared from parts of its former range. Protect private land where the species occurs through cooperative agreements with landowners (USFWS).
|Citation:||BirdLife International 2012. Dendroica angelae. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 08 March 2014.|
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