|Scientific Name:||Xenopus longipes Loumont & Kobel, 1991|
|Taxonomic Source(s):||Frost, D.R. 2016. Amphibian Species of the World: an Online Reference. Version 6.0 (31 March 2016). New York, USA. Available at: http://research.amnh.org/herpetology/amphibia/index.html.|
|Taxonomic Notes:||Uniquely among vertebrates (except Xenopus eysoole, X. kobeli and X. ruwenzoriensis), this is a dodecaploid species, and it is therefore of considerable scientific interest. It was probably formed by both hybridization and polyploidization (Loumont and Kobel 1991).|
|Red List Category & Criteria:||Critically Endangered B1ab(iii,v)+2ab(iii,v) ver 3.1|
|Assessor(s):||IUCN SSC Amphibian Specialist Group|
|Contributor(s):||Blackburn, D., Measey, G.J., Tinsley, R. & Doherty-Bone, T.|
|Facilitator/Compiler(s):||Angulo, A., Luedtke, J., Hobin, L.|
Listed as Critically Endangered because its extent of occurrence (EOO) and area of occupancy (AOO) is 2 km2, it occurs in one threat-defined location, and there is a projected decline in the number of mature individuals, due to the high likelihood of a fish introduction into Lake Oku, habitat degradation which is causing subsequent decline in the quality of the water in the lake, and perhaps the compounded effects of disease.
|Previously published Red List assessments:|
|Range Description:||This species is endemic to Lake Oku situated at 2,200 m Asl on Mount Oku in western Cameroon. While it might occur in other crater lakes in the Cameroon highlands, it was not recorded in these lakes during surveys in 2012 (T. Doherty-Bone pers. comm. July 2012). The area of the lake is only 243 hectares (Kling 1988). Its EOO and AOO is 2 km2.|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||This species is abundant in Lake Oku. However, since 2006, recurring mass mortality events have been recorded. These remain enigmatic and might be due to disease, although testing for Bd and Ranavirus has been negative on multiple occasions or of low prevalence (Blackburn et al. 2010, Doherty-Bone et al. 2013, Quock et al. 2014, Hirschfeld et al. 2016). Recent surveys still suggest that the species occurs in large numbers (T. Doherty-Bone unpubl. data).|
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||Lake Oku is a shallow, oligotrophic lake completely surrounded by montane rainforest. This species is entirely water-dependent, quite inept on land, and is the main aquatic vertebrate in the lake, likely filling an ecological niche similar to an omnivorous or insectivorous fish.|
Breeding ecology is not clear as breeding behaviour has not been consistently observed, tadpoles are rarely observed alive in the lake and adults are the same size as metamorphs (T. Doherty-Bone pers. comm. February 2017). When tadpoles have been found washed up at lake shore, this has been between July and October. In captivity, the larvae took six months and longer to metamorphose (Michaels et al. 2015).
|Continuing decline in area, extent and/or quality of habitat:||Yes|
|Movement patterns:||Not a Migrant|
|Use and Trade:||
There are no records of this species being utilized. Experts were concerned about the increasing international interest in this species and worried the species would be harvested for international trade in the near future, if it is not already occurring. However, this is based on one incident of an animal dealer contacting a Cameroonian field assistant for collection, which turned out to be merely prospective (T. Doherty-Bone pers. comm. February 2017).
One potential threat to this species would appear to be the risk of introduction of fish into Lake Oku, which could wipe out this restricted-range species. Such a scenario is highly plausible given the high protein demands of surrounding communities. However there have been no official fish introductions into the lake as of yet, and fish introduction continues to be blocked by the local forestry and wildlife office (which manages the protected area encompassing the lake) and opposed by traditional authorities (Fon and elders) and local environmentalists who also encourage the abstinence of fish introduction (T. Doherty-Bone pers. comm. November 2016). Surveys between 2006–2012 documented an unknown disease associated with mass mortality events, possibly involving a pathogen (Doherty-Bone et al. 2013).
Another threat includes the degradation of the forest around Lake Oku, which could alter the water quality though siltation and nutrient pollution. This occurs through livestock grazing and forest loss due to wood cutting and infrastructure developments. These are likely to be exacerbated by increases in visitors to the lake as a result of these developments, and if unregulated could induce increased demands for fuel wood and garbage accumulation (T. Doherty-Bone pers. comm. February 2017). There have also been cases when visitors to the lake have washed clothes using chemical detergents. Loss of forest around the lake could also increase run-off of chemicals from vehicles on the road above the lake (T. Doherty-Bone pers. comm. February 2017).
A retrospective study analysing amphibian population declines (between 2004–2012) and Bd emergence (in 2008) on Mount Manengouba and Mount Oku in Cameroon suggest that chytridiomycosis has driven community level declines of anuran biodiversity in these hotspot areas (Hirschfeld et al. 2016). This species was not tested for Bd during Hirschfeld et al.(2016) study so it is not known whether chytridiomycosis is a threat, but other species in the genus had mixed results.
Lake Oku and its surrounding forest are protected by the national governement-sanctioned Kilum-Ijim Plantlife Sanctuary, restricting access to the lake; though enforcement is difficult and even controversial. In response to the 2004 assessment of Xenopus longipes, a captive-breeding programme is being attempted by European zoos (London, Antwerp and Cologne) in view of the risk of a catastrophic collapse of the population (Browne et al. 2009). The first successful captive breeding of this species was achieved by ZSL London Zoo in 2014 (Michaels et al. 2015). A conservation project was also conducted on Mount Oku for several years by BirdLife International, which involved community management of mountain forest involving the local villages. However, the project ended in the mid-2000s (N. Gonwouo pers. comm. June 2012).
The mysterious disease that has affected this species has been monitored since its discovery in 2006. However, its cause and long-term consequences are still not understood other than its apparent stability amid a numerically abundant frog population (Doherty-Bone et al. 2013). While chytrid is present in the region, it is apparently not affecting this species and is not the culprit of the observed die-offs. Since 2008, a project has monitored the abundance of frogs, occurrence of disease, fluctuations of environmental parameters in the lake, and raised awareness and engagement with local communities (Doherty-Bone 2015). The lake is situated just outside the boundary of a proposed Faunal Reserve on Mount Oku.
A review and update of the 2013 conservation action plan is due (T. Doherty-Bone pers. comm. February 2017). Future actions will likely include the continuation of disease monitoring, increasing community involvement and awareness, the continuation of ex-situ breeding programmes, and improving the protection of Lake Oku (prevention of fish stocking) and its surrounding forest. Recent development above the lake also indicate engagement with those stakeholders (from outside the region) is necessary to minimise current and future developments that could over-rule local decisions for protection (T. Doherty-Bone pers. comm. February 2017).
Research is required to establish the cause of the observed die-offs, to determine the spatial distribution of the frog across the lake and estimate of minimum viable populations, to understand the broader ecology of Lake Oku (such as food webs and submerged vegetation), to understand the reproductive ecology of this species, to see whether there is the potential for other Xenopus species to colonise Lake Oku and out-compete this species, for socio-economic appraisals of community and opportunities for sustainable protection of the lake, to establish the effect by Bd infection on this species, and to determine the effectiveness of conservation interventions (T. Doherty-Bone pers. comm. February 2017). There is also the need to remain vigilant to harvest for international trade (T. Doherty-Bone pers. comm. February 2017).
Blackburn, D.C., Evans, B.J., Pessier, A.P. and Vrendenburg, V.T. 2010. An enigmatic mortality event in the only population of the Critically Endangered Cameroonian frog Xenopus longipes. African Journal of Herpetology 59(2): 1-12.
Browne R.K., Blackburn D.C. and Doherty-Bone T.M. 2009. Species profile: Lake Oku clawed frog (Xenopus longipes). Amphibian Ark Taxon Management Plan.
Doherty-Bone, T. 2015. From surveying to engagement to action planning: working to conserve amphibians on Mt Oku, Cameroon. Froglog 115: 60-63.
Doherty-Bone, T.M. 2007. Belo-Community Herpetological and Conservation Project. University of Aberdeen, Aberdeen.
Doherty-Bone, T.M. 2011. Unravelling the mysteries of Lake Oku, where the frog is “Fon” (king). FrogLog 97: 28-30.
Doherty-Bone, T.M., Ndifon, R.K., Nyingchia, O.N., Landrie, F.E., Yonghabi, F.T., Duffus, A.LJ., Price, S., Perkins, M., Bielby, J., Kome, N.B., LeBreton, M., Gonwouo, L.N. and Cunningham, A.A. 2013. Morbidity and mortality of the Critically Endangered Lake Oku clawed frog Xenopus longipes. Endangered Species Research 21: 115-128.
Gartshore, M.E. 1986. The status of the montane herpetofauna of the Cameroon highlands. In: Stuart, S.N. (ed.), Conservation of Cameroon Montane Forests, pp. 204-240. International Council for Bird Preservation, Cambridge, U.K.
Hirschfeld, M., Blackburn, D.C., Doherty-Bone, T.M., Gonwouo, L.N., Ghose, S. and Rödel, M.-O. 2016. Dramatic Declines of Montane Frogs in a Central African Biodiversity Hotspot. PLoS ONE 11(5).
IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-2. Available at: www.iucnredlist.org. (Accessed: 14 September 2017).
Kling, G.W. 1988. Comparative transparency, depth of mixing, and stability of stratification in lakes of Cameroon, West Africa. Limnology and Oceanography 33(1): 27-40.
Kobel, H.R., Barundun, B. and Thiebaud, C.H. 1998. Mitochondrial rDNA phylogeny in Xenopus. Herpetological Journal 8: 13-17.
Loumont, C. and Kobel, H.R. 1991. Xenopus longipes sp. nov., a new polyploid pipid from western Cameroon. Revue Suisse de Zoologie 98: 731-738.
Michaels, C.J., Tapley, B., Harding, L., Bryant, Z., Grant, S., Sunter, G., Gill, I., Nyingchia, O. and Doherty-Bone, T. 2015. Breeding and rearing the Critically Endangered Lake Oku Clawed Frog (Xenopus longipes Loumont and Kobel 1991). Amphibian and Reptile Conservation 9(2): 100-110.
Tinsley, R.C. and Kobel, H.R. 1996. The Biology of Xenopus. Zoological Society of London, Clarendon Press, London.
|Citation:||IUCN SSC Amphibian Specialist Group. 2017. Xenopus longipes. The IUCN Red List of Threatened Species 2017: e.T58176A3067255.Downloaded on 22 April 2018.|
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