Colombobalanus excelsa
(Lozano, Hern.Cam. & Henao) Nixon & Crepet
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Calcul du tissu écologique de Colombobalanus excelsa.
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Liste rouge IUCN
EN · En dangercritères B2ab(iii,v)↘Décroissante- Évaluation
- 2020 · v3.1
- Altitude
- 1400 – 2200 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Subpopulations in four forest fragments along Serranía Peñas Blancas, in the municipalities of Tinamá and Acevedo, in Huila, had an average density of 746 individuals per hectare (Aguirre-Acosta and Botero 2018). Vegetation samples collected from those subpopulations also showed low genetic diversity, and again unique alleles (Aguirre-Acosta et al. 2013), probably as a result of severe fragmentation and isolation.
In the southern part of Huila department, where the main area of the black oak distribution is found, GIS studies using spectral signatures, estimated a total area of 40,000 ha for this species. Field studies later confirmed the presence of forest fragments of up to 100 ha and that the species is only found on the western side of the Eastern Cordillera and not on the eastern side facing the Amazon region.
In contrast, subpopulation studies carried out in Santander, in the municipality of Charalá, indicated that black oaks are found in very small patches of less than one hectare in size and along narrow riparian corridors. This study also found single trees in cattle producing pastures, as evidence of major processes of deforestation of black oak forests in that area.
The subpopulation in Virolín, near the Flora and Fauna Sanctuary, in Santander, were found to be seriously affected by deforestation; as a result the total area of black oak forest in that region is declining due to anthropogenic factors (Cárdenas and Salinas 2007). In the municipality of Amalfi, Antioquia, Ariza et al. (2009) found isolated trees, but in Serranía de San Lucas, the subpopulation most recently found, there are monospecific forest patches of significant sizes (Andrés Avella, pers. com.). There is an urgent need to explore that region that may turn out to be as important as the one in Huila. Avella found black oak forest patches in good conditions, but also observed evidence of deforestation near urban and mining centres.
Other subpopulations in Santander, Antioquia and Valle del Cauca have not been studied.
Menaces identifiées(4 menaces classées CMP-IUCN)
1_1Housing & urban areasUnknownUnknownOngoing2_1_2Small-holder farmingUnknownUnknownOngoing3_2Mining & quarryingUnknownUnknownOngoing5_3_1Intentional use: (subsistence/small scale) [harvest]UnknownUnknownOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Habitats préférentiels (classification IUCN)
1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Black oak forest remnants located in national parks and nature reserves are being protected. That is the case of those in Cueva de los Gúacharos and Farallones de Cali National Parks, and in the Flora and Fauna Sanctuary Guantentá-Río Fonce, in Santander. Several regional efforts are effectively protecting some black oak forest remnants; in Alto Bellavista, Huila, local coffee producing communities are protecting black oak forests remnants (Aguirre-Acosta and Botero, 2018) interested in ensuring the future of the watersheds and their biodiversity.
The main subpopulation in the Huila Department has now a better chance of being protected. The Huila regional environmental authority, Corporación Autónoma Regional del Alto Magdalena (CAM), is now coordinating the implementation of a conservation and management plan for black oak forests (Botero-Fernández et al. 2010) in that department. As part of that plan, the area of distribution of black oaks was given a special conservation status in 2018; Serranía de Peñas Blancas Integrated Management District, which covers the entire black oak forest subpopulations in the Department outside Cueva de los Guácharos National Park. In addition, under the conservation and management plan, research has been carried out on asexual reproduction and restoration plans for the species.
Although improvements have been made in the black oak conservation in Huila, deforestation is still a major threat. While producing the Forest Management Plan for that department (PGOF) in 2010, Fandiño and others estimated deforestation rates between 5.000 and 10.000 ha per year. This study, however, did not examine regional or forest type differences in those deforestation rates, but did emphasize the need for more careful monitoring of Black Oak areas.
The most northern subpopulations in the Antioquia and Bolivar provinces (Amalfi and San Lucas) have no protection and they have threats from habitat destruction and overexploitation.
Some ex situ efforts have been initiated but with mixed results. The Bogota Botanical Garden has at least one individual, but there is no recent assessment to confirm its status. Other exercises of ex situ conservation were carried out in the campus of the National University of Colombia, Medellin, and in the municipality of Santo Domingo, in Huila, carried out by CAM, but they were not successful. Finally, there is a report on ex situ conservation experiences in the Cachalú Reserve in the department of Santander, led by Fundación Natura. In this ex situ experience, conservation strategies were developed within productive systems in the Corredor Guantiva - La Rusia - Iguaque, in the municipality of Arcabuco, department of Boyacá.
In Colombia, the Black Oak was officially included in the list of endangered plants in a decree by the Ministry of Environment and Sustainable Development in 2014. That decree also instructs government institutions dealing with endangered biodiversity to develop and implement conservation plans for those species in the list.
Stress écologiques (12)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance
Usage & commerce (1)Use & Trade — IUCNExpert
9Construction or structural materials
Priorités de recherche (2)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (23)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-1. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 19 March 2020).
- Aguirre-Acosta, N. and Botero-Echeverri, J.E. 2018. Estructura poblacional y distribución espacial del roble negro (<i>Colombobalanus excelsa</i>, Fagaceae), especie endémica, en fragmentos de bosque andino colombiano. <i>Revista de Biologia Tropical (International Journal of Tropical Biology </i> 66(2): 486-494.
- Avella A., Rangel, O. and Parra, C. 2017. Bosques de Roble Negro <i>Colombobalanus excelsa</i> (Lozano, Hern. Cam & Henao) Nixon & Crepet en Colombia: Sintaxonomía, composición florística y estructura. In: Rangel, J.O. (ed.), <i>Colombia Diversidad Biótica XV. Los bosques de roble (Fagaceae) en Colombia. Composición florística, estructura diversidad y conservación</i>, pp. 149-214. Colombia Diversidad Biótica XV. Los bosques de roble (Fagaceae) en Colombia. Composición florística, estructura diversidad y conservación, Bogotá.
- Moreno, J. S. 2014. Estructura poblacional del roble negro (Colombobalanus excela) en el Valle del Cauca, una herramienta para la formulación de una estrategia para su conservación. Facultad de Ciencias naturales, Biología, Universidad Icesi.
- Aguirre-Acosta, N., Palacio-Mejía, J.D, Barrios-Leal, D.J. and Botero, J.E. 2013. Diversity and Genetic Structure of the Monotypic Genus <i>Colombobalanus</i> (Fagaceae) in Southeast of Colombian Andeans. <i>Caldasia</i> 35(1): 123-133.
- Dávila, E. D., Alvis, J.F. and Ospina, R. 2012. Distribución espacial, estructura y volúmen de los bosques de roble negro (Colombobalanus excelsa (Lozano, Hern. Cam. & Henao) Nixon & Crepet) en el Parque Nacional Natural Cueva de los Guácharos. <i>Colombia Forestal</i> 15(2): 207-214.
- Sun, W.B., Zhou, Y., Han, C.Y., Chen, G., Zheng, Y.L. 2011. <i>Trigonobalanus</i>. <i>Wild Crop Relatives: Genomic and Breeding Resources, Forest Trees</i>, Springer-Verlag, Berlin Heidelberg.
- Parra, C.A., Diez, M.C. and Moreno, F. 2011. Regeneración natural del Roble Negro (<i>Colombobalanus exelsa</i>, Fagaceae) en dos poblaciones de la cordillera Oriental de los Andes, Colombia. <i>Revista Facultad Nacional de Agronomía - Medellín</i> 64(2): 6175-6189.
- Botero, J.E., López, A.M., Espinosa, R. and Casas C. 2010. <i>Aves de zonas cafeteras del sur del Huila</i>. Cenicafé, Chinchiná, Caldas.
- Botero-Fernández, V., Diez, M.C., Parra, C., Serna, J., Adames, L. and Rodríguez, N. 2010. Plan de Conservación para la especie amenazada roble negro - <i>Colombobalanus excelsa</i> (Lozano, Hdz-C & Henao) Nixon & Crepet, en los ecosistemas de interés del departamento del Huila. Universidad Nacional de Colombia sede Medellín.
- Forero, J. 2010. “Colombian Family Farmers” Adaptations to New Conditions in the World Coffee Market. <i>Latin American Perspectives</i> 37(2): 93-110.
- Paiba, J.E. 2009. Avifauna en tres robledales del Huila. Facultad de Ciencias Exactas y Naturales, Universidad de Caldas.
- Arroyave, M. 2007. Análisis de la diversidad genética de la especie vulnerable <i>Colombobalanus excelsa</i> (Lozano <i>et al.</i>) Nixon & Crepet (Fagaceae) por medio de marcadores moleculares microsatélites. Universidad del Valle.
- Cárdenas, D. and Salinas, N. 2007. Libro rojo de planta de Colombia. Especies maderables amenazadas: Versión Preliminar I parte. In: Cardenas, D. and Salinas, N. (eds), <i>Serie de Libros Rojos de Especies Amenazadas en Colombia</i>, Instituto Amazónico de Investigaciones SINCHI, Ministerio de Ambiente, Vivienda y Desarrollo Territorial, Bogotá. D.C.
- González, Y., Coca, A. and Cantillo, E. 2007. Estructura y Composición Florística de la vegetación del Corredor Biológico entre los Parques Nacionales Naturales Puracé y Cueva de Los Guácharos. <i>Revista Colombia Forestal</i> 10(20): 40-78.
- Manchola, H. and Parra, C. 2006. Los robles como objetos de conservación del proyecto Corredor Biológico entre los PNN Puraé - Cueva de los Guácharos. In: Solano, C. and Vargas, N. (eds), Memorias I Simposio Internacional de Roble y Ecosistemas Asociados. Fundación Natura-Pontificia Universidad Javeriana, Bogotá.
- Etter, A., McAlpine, C., Wilson, K., Phinn, S. and Possingham, H. 2006. Regional patterns of agricultural land use and deforestation in Colombia. <i>Agricultural, Ecosystems & Environment</i> 114: 369-386.
- Palacio-Mejía, J.D., Fernández-Manjarrés, J.F., Sánchez-Baracaldo, P. and Villafañe-Palau C. 2005. Estudio comparativo de la diversidad genética y divergencia evolutiva entre la especie vulnerable <i>Colombobalanus excelsa</i> (Lozano, <i>et al</i>.) Nixon & Crepet y el roble común <i>Quercus humboldtii</i> Bondpl. Implicaciones para la biología de la conservación. Palmira Escuela de Posgrados, Universidad Nacional de Colombia.
- Arango, N., Matallana, C. and Morales, M. (eds). 2002. <i>Caracterización biótica corredor oriental de conservación para el SIRAP Huila</i>. Instituto Alexander von Humboldt (IAVH).
- Calderon, E. (compiler) 1997. Lista de plantas Colombianas en peligro. July 1997 Version. Instituto de Investigacino de Recursos Biologicas Alexander von Humboldt. (unpublished).
- Centro Do Datos Para la Conservacion-CDC-CVC. 1986. Lista preliminar de plantas especiales del centro de datos para la conservacion, CDC-CVC (unpublished).
- Eslava, J.A., López, V.A. and Olaya, G. 1986. Contribución al conocimiento del régimen térmico y pluvio-métrico de Colombia. <i>Colombia Geográfica</i> 12(2): 53-118.
- Lozano, C., Hernández, J. and Henao, J. 1979. Hallazgo del género <i>Trigonobalanus</i> Forman (Fagaceae) en el Neotrópico I. <i>Caldasia</i> 12(60): 517-537.
Évaluateurs & contributeurs (3)Personnes ayant contribué à l'évaluation IUCNExpert
Aguirre-Acosta, N., Parra Aldana, C.A. & Botero, J.E. 2020. Trigonobalanus excelsa. The IUCN Red List of Threatened Species 2020: e.T32076A137102918. Accessed on 05 May 2026.
Distribution mondiale
Phénologie
Consulter sur les bases externes
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (1)— redirigent vers cette page
- Trigonobalanus excelsaLozano, Hern.Cam. & Henao
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).