|Scientific Name:||Melanerpes herminieri|
|Species Authority:||(Lesson, 1830)|
|Taxonomic Source(s):||del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Lynx Edicions BirdLife International.|
|Red List Category & Criteria:||Near Threatened ver 3.1|
|Reviewer(s):||Butchart, S. & Symes, A.|
|Facilitator/Compiler(s):||Wege, D., Isherwood, I., Benstead, P., Mahood, S.|
This species has a very small range in which habitat degradation is causing the population to decline. However, the range is not yet severely fragmented or restricted to few locations. For these reasons, the species is classified as Near Threatened.
|Previously published Red List assessments:||
|Range Description:||Melanerpes herminieri is endemic to Guadeloupe (to France) and inhabits the two main islands, Basse-Terre and Grande-Terre.|
|Continuing decline in area of occupancy (AOO):||Yes|
|Extreme fluctuations in area of occupancy (AOO):||No|
|Estimated extent of occurrence (EOO) - km2:||1500|
|Continuing decline in extent of occurrence (EOO):||Unknown|
|Extreme fluctuations in extent of occurrence (EOO):||No|
|Continuing decline in number of locations:||Yes|
|Extreme fluctuations in the number of locations:||No|
|Upper elevation limit (metres):||1000|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The population was estimated to comprise 7,920 pairs in 381 km2 on Basse-Terre, and 2,410 pairs in 135 km2 on Grande-Terre in 1994 (Villard and Rousteau 1998). Surveys in 2007 revealed no significant change, but a different methodology calculated a total population of 8,469 pairs (Villard et al. 2010). The population is therefore estimated to number at least 16,000 mature individuals, roughly equivalent to 24,000 individuals in total.
Trend Justification: The population is stable (Villard et al. 2010).
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||It inhabits semi-deciduous forest on igneous and clay ground, evergreen forest, mangroves and swamp forest (Villard and Rousteau 1998), and excavates nest holes in the trunks of dead trees (Raffaele et al. 1998). It occurs from sea-level to the tree-line at 1,000 m, but is most common at 100-700 m (Winkler et al. 1995, Villard and Rousteau 1998). Habitats with the highest estimated population densities were seasonal evergreen secondary growth forest, followed by swamp forest and rainforest (Villard et al. 2010). Food items taken include a variety of invertebrates, vertebrates and fruit (Villard 2000).
|Continuing decline in area, extent and/or quality of habitat:||Yes|
|Generation Length (years):||5.1|
|Movement patterns:||Not a Migrant|
|Major Threat(s):||Clear-cutting and the removal of dead trees are the main threats, but damage from hurricanes, road construction, airport enlargement and land development are all concerning (Raffaele et al. 1998, Villard and Rousteau 1998, Villard et al. 2010). Introduced rats may also be a problem (Raffaele et al. 1998).|
Conservation Actions Underway
About 27% of remaining habitat is protected within the Guadeloupe national park (Villard et al. 2010). Conservation Actions Proposed
Monitor populations regularly. Discourage the removal of dead trees. Discourage clear-cutting and the siting of new roads and airports in valuble habitats. Investigate the impact of rats on nesting success.
|Citation:||BirdLife International. 2012. Melanerpes herminieri. The IUCN Red List of Threatened Species 2012: e.T22680804A40623196. . Downloaded on 28 May 2016.|
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