|Scientific Name:||Tauraco bannermani|
|Species Authority:||(Bates, 1923)|
|Red List Category & Criteria:||Endangered B1ab(i,ii,iii,iv,v) ver 3.1|
|Contributor/s:||DeMarco, J., Forboseh, P., Fotso, R., Maisels, F., Thomas, D. & Stewart, K.|
|Facilitator/s:||Benstead, P., Ekstrom, J., Pilgrim, J., Shutes, S., Symes, A., Taylor, J.|
This species is listed as Endangered because it has a very small range, which is severely fragmented and suffering a continuing decline owing to pressure from human use on its montane forest habitat.
|Range Description:||Tauraco bannermani is mainly restricted to the Bamenda Highlands in western Cameroon, but small populations exist on nearby Mt Mbam (Njabo and Languy 2000) and, most recently discovered, at Fossimondi and Fomenji to the south-west. It is only likely to survive if the Kilum-Ijim forest, the largest remaining montane forest area in the Bamenda Highlands, is preserved (D. Thomas in litt. 1996). Research in 1994-1995 found the species in several remaining forest remnants in the Bamenda Highlands and seemingly able to survive in very small forest fragments (<1 km2) (McKay and Coulthard 1996). However, follow-up surveys in 2000 found some of these forest fragments had almost completely disappeared, with T. bannermani either absent or with only a few pairs remaining (Njabo and Languy 2000). In Kilum-Ijim, it is unlikely that more than 1,000-1,500 pairs occur (Forboseh and Ikfuingei 2001).|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The total population is estimated in the range 2,500-9,999 individuals based on data given by Forboseh and Ikfuingei (2001). This equates to 1,667-6,666 mature individuals, rounded here to 1,500-7,000 mature individuals.|
|Habitat and Ecology:||It is an arboreal frugivore of montane forest (McKay 1994). It can survive in degraded and secondary forest as long as sufficient tall, fruiting trees remain (Stuart 1986). At lower altitudes, it is replaced by its congener, the Green Turaco T. persa, which is found in more open forest or scrub (McKay 1994, McKay and Coulthard 1996). It would appear to move to higher altitudes (2,200-2,600 m) during the breeding season, probably to exploit seasonal fruiting patterns (Forboseh and Ikfuingei 2001).|
The greatest threat to this species is habitat loss: the Kilum-Ijim forest halved in area between 1963 and 1986. Following changes to a major long-term conservation project in 2004, it is reported that the threats of habitat loss and degradation at Kilum-Ijim have increased (P. Forboseh in litt. 2007, R. Fotso in litt. 2007, Stewart 2009). Forest fires are responsible for the greatest proportion of habitat loss (P. Forboseh in litt. 2003), for example c.500 ha of forest burnt around Lake Oku in March 2000 (J. DeMarco in litt. 2000). It is also under serious threat from forest clearance for agriculture, grazing, firewood and timber, with birds surviving in forest fragments in imminent danger of extinction (McKay and Coulthard 1996), particularly due to their reluctance to cross open habitats (Njabo and Languy 2000). The species is hunted for its feathers, which are given as awards in local ceremonies (K. Stewart in litt. 2012).
Conservation Actions Underway
CITES Appendix II. Local communities are actively engaged in conserving montane forest, with support from the Kilum-Ijim Forest Project. However, there is now reportedly a lack of adequate conservation action taking place at Kilum-Ijim, despite the presence of many forest management institutions around the forest (P. Forboseh in litt. 2007). Community-based conservation activities were extended to other forest fragments in the Bamenda Highlands in 2000 (J. DeMarco in litt. 2000, P. Forboseh in litt. 2003). Conservation Actions Proposed
Study ecological constraints to its survival including seasonal food requirements, size of forest patches, tolerance of habitat degradation (Forboseh and Ikfuingei 2001) and competition with T. persa (Dowsett-Lemaire and Dowsett 1998c, J. DeMarco in litt. 2000). Conduct surveys to improve knowledge about the species's population size. Take measures to prevent forest fires (F. Maisels in litt. 1998) and educate communities about the magnitude of the forest fire problem (F. Maisels in litt. 1998). Protect as many as possible of the remaining forest fragments in the Bamenda Highlands (J. DeMarco in litt. 2000). Develop strategies for restoring larger blocks of natural forest and connecting corridors (J. DeMarco in litt. 2000) and establish captive breeding populations to assist in the recolonization of areas and the supplementation of existing populations.
|Citation:||BirdLife International 2013. Tauraco bannermani. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 10 March 2014.|
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