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040
Colombian inter-Andean slopes
Country/Territory Colombia
Area 48,000 
Altitude 1,000 - 2,500m  
Priority critical 
Habitat loss major 
Knowledge incomplete 


General characteristics 

Lying within the Andes of Colombia, this EBA embraces the slopes of the Pata, Cauca and Magdalena valleys. At the head of the Magdalena valley it extends on both slopes onto the southernmost end of the East Andes (south of EBA 038). It extends across the Central Andes at a low narrow point (between Manizales and Medelln at c.540) to the eastern slope of the Central Andes, thus embracing most of the western side of the Magdalena valley and Central Andean foothills. Although traditionally regarded as two separate centres of endemism (the Cauca and Magdalena centres), many of the restricted-range species occur in both valley systems, and they are thus considered here to comprise a single EBA.

The EBA is characterized by the mid-elevation (subtropical) evergreen forests of the Andean foothills at 1,000-2,500m. The species confined to the drier vegetation of the valley floors (Colombian inter-Andean valleys, EBA 039) may overlap altitudinally with some of those from the humid forest, especially where clearance has resulted in dry scrub spreading up the valley sides. Also adjacent is the North Central Andes (EBA 042), whose species sometimes overlap altitudinally with species on the slopes of the Central Andes, although the birds of the North Central Andes generally occupy higher areas (2,000-3,600m) and are confined to humid upper montane forest and cloud forest.

Restricted-range species 

The species primarily occupy humid foothill and lower montane forest with associated edge and secondary vegetation, mainly at c.1,200-2,500m.

A number of species from this EBA are also found on the Pacific slope of the West Andes within the Choc (EBA 041). Penelope perspicax occurs in just a few low passes and is thus regarded as confined to the inter-Andean area, much as the species found in (presumably the same) low passes on the eastern side of the West Andes are taken to be restricted to the Choc (see EBA 041). Bangsia melanochlamys is primarily a bird of the Pacific slope of the West Andes (EBA 041), but is known from a disjunct population on the northern and western slopes of the Central Andes in Antioquia department (where it has however been recorded from very few localities, and not since 1948) (Collar et al. 1992). Tinamus osgoodi has a curious distribution: the subspecies hershkovitzi is known from just two localities within this EBA (one is the Cueva de los Gucharos National Park), and the only other population lies c.2,000km south in the Peruvian East Andean foothills (EBA 053).

Birds which are almost certainly Grallaria alleni have been seen and tape-recorded in the Cordillera de Guacamayo in Ecuador (P. Coopmans in litt. 1995), which would extend the species' range into the North Central Andes (EBA 042). A specimen of Black Inca Coeligena prunellei from Salento in the Central Andes (Collar et al. 1992) is now suspected to be in error (A. J. Negret in litt. 1994), and the species has therefore been omitted from consideration for this EBA (it is thus confined to the Colombian East Andes, EBA 038).

Species IUCN Category
Black Tinamou (Tinamus osgoodi)  VU 
Cauca Guan (Penelope perspicax)  EN 
Chestnut Wood-quail (Odontophorus hyperythrus)  NT 
Tolima Dove (Leptotila conoveri)  EN 
Blossomcrown (Anthocephala floriceps)  VU 
Rufous-vented Whitetip (Urosticte ruficrissa)  LC 
Yellow-headed Manakin (Xenopipo flavicapilla)  NT 
Black-chested Fruiteater (Pipreola lubomirskii)  LC 
Schwartz's Antthrush (Chamaeza turdina)  LC 
Moustached Antpitta (Grallaria alleni)  VU 
Hooded Antpitta (Grallaricula cucullata)  VU 
Red-bellied Grackle (Hypopyrrhus pyrohypogaster)  VU 
Yellow-headed Brush-finch (Atlapetes flaviceps)  EN 
Dusky-headed Brush-finch (Atlapetes fuscoolivaceus)  NT 
Black-and-gold Tanager (Bangsia melanochlamys)  VU 
Multicoloured Tanager (Chlorochrysa nitidissima)  VU 
Turquoise Dacnis (Dacnis hartlaubi)  VU 

Important Bird Areas (IBAs)

IBA Code Site Name Country
  Corredor Ladera Chipre - Alcazares - Arenillo  Colombia 
  Finca Chupadero  Colombia 
  Finca La Cascada  Colombia 
  Jardín  Colombia 
CO023  Parque Nacional Natural Las Orquídeas  Colombia 
CO024  Bosques Montanos del Sur de Antioquia  Colombia 
CO028  Reserva Forestal Yotoco  Colombia 
CO031  Farallones de Cali Natural National Park (Parque Nacional Natural Farallones de Cali IBA)  Colombia 
CO036  La Forzosa-Santa Gertrudis  Colombia 
CO037  San Sebastián  Colombia 
CO039  Embalse de San Lorenzo y Jaguas  Colombia 
CO043  La Victoria  Colombia 
CO045  Reserva Hidrográfica, Forestal y Parque Ecológico de Río Blanco  Colombia 
CO047  Bosques del Oriente de Risaralda  Colombia 
CO050  Cañón del Río Barbas y Bremen  Colombia 
CO051  Finca la Betulia Reserva la Patasola  Colombia 
CO052  Reserva Natural Ibanasca  Colombia 
CO054  Cañón del Río Combeima  Colombia 
CO055  Cuenca del Río Toche  Colombia 
CO056  Reserva Natural Semillas de Agua  Colombia 
CO057  Páramos y Bosques Altoandinos de Génova (part of Loros Andinos Natural Reserve AZE)  Colombia 
CO058  Lagunas Bombona y Vancouver  Colombia 
CO063  Puracé (Parque Nacional Natural Puracé IBA)  Colombia 
CO064  Reserva Natural Meremberg  Colombia 
CO065  Parque Nacional Natural Cueva de los Guácharos  Colombia 
CO076  Serranía de las Quinchas  Colombia 
CO132  Haciendas Ganaderas del Norte del Cauca  Colombia 
CO139  Serranía de los Paraguas  Colombia 
CO141  Serranía de las Minas  Colombia 

Threats and conservation 

Both the Cauca and Magdalena valleys (and the mountain slopes bounding them) have been severely deforested over a long history of human colonization, and the area is now characterized by remnant (often secondary) forest patches, pasture, coffee, banana plantations, etc. (Collar et al. 1992, Wege and Long 1995). In the Cauca valley at the northern end of the West Andes, extensive forest destruction for pasture has confined remaining forest to ridge crests and isolated patches, with humid subtropical forest almost totally gone from the middle part of the valley (e.g. in the Quindo watershed). Similarly, at the northernmost end of the Central Andes, forest destruction has been near-complete, with extensive clearance around Medelln leaving just remnant patches of primary and old secondary growth (among coffee and Pinus patulla plantations) in urgent need of protection. At the head of the Magdalena valley, forest has given way to coffee, bananas and sugar-cane, with the western slope of the southernmost East Andes (e.g. Cueva de los Gucharos National Park) increasingly threatened by human encroachment and opium production (Wege and Long 1995).

The widespread (though localized) destruction of natural vegetation in this EBA has resulted in all but two of the restricted-range species being considered either threatened (nine species) or Near Threatened (five species), with one species classified as Data Deficient. The widespread (though localized) but threatened Yellow-eared Parrot Ognorhynchus icterotis (classified as Critical) and Golden-plumed Parakeet (Vulnerable) also occur in this EBA, and similarly are threatened almost exclusively by forest loss.

Sixteen Key Areas for the threatened birds have been identified in this EBA, including important protected areas such as Los Nevados, Cueva de los Gucharos and Munchique National Parks, Ucumar Regional Park, Alto Quindo Acaime Natural Reserve and Caon del Quindo Natural Reserve, Bosque de Yotoco Reserve and Tambito Nature Reserve (Wege and Long 1995). With such widespread forest destruction, the value of these areas cannot be overstated as critically important sites for conservation.

Recommended citation  BirdLife International (2013) Endemic Bird Area factsheet: Colombian inter-Andean slopes. Downloaded from http://www.birdlife.org on 19/06/2013

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