Mount Opay

Hosere Opay, Hosere Ziver, Mount Tourou

CMNTIPA047
Mount Opay

Country: Cameroon

Administrative region: Far North (Region)

Central co-ordinates: 10.86040 N, 13.77470 E

Area: 60km²

Qualifying IPA Criteria

A(i)Site contains one or more globally threatened species

IPA assessment rationale

Due to the small nature of the site and its assumed heavily degraded condition, populations of globally threatened taxa recorded from the site may not meet the IPA criteria at the site. However, the site may qualify as a potential IPA through being a nationally and globally significant site for Euphorbia desmondii and through possible nationally important populations of Khaya senegalensis and Monanthotaxis elegans. The site is likely to qualify as a threatened habitat type under criterion C if surveying can establish that the habitat is capable of survival or restoration.

Site description

Mount Opay and neighbouring Mount Ziver are the highpoint of the Mandara Mountains, a range of rain-intercepting, granitic mountains in the otherwise largely arid Far North Region of Cameroon. The Mandara Plateau mosaic is a unique mapping unit in the classification of White (1983) and Olson et al. (2001), sharing affinities with the Sudanian and Afromontane regional centres of endemism. The area has long been densely populated and is ethnically diverse. Seasonal transhumance and terrace cultivation is used to improve the yields of the steep, porous and often infertile terrain. Natural vegetation is sparse and much degraded. The site itself is close to the Nigerian border, north of Mokolo and about 60 km west of Maroua.

Botanical significance

The Mandara mountains are recognised as a major phytogeographical unit and ecoregion, combining arid Sudano-Sahelian vegetation with outlying moist forest and Afromontane elements (White 1983; Olson et al. 2001; Seymour 2004). Only at higher altitudes (above 1200-1300 m) are the latter elements notable, with species such as Olea capensis and Pittosporum viridiflorum (White, 1983). One of the most important species recorded is Euphorbia desmondii (DD) which is only recorded from a handful of other locations in northern Nigeria and Cameroon and in Central Africa Republic (Rivers, 2021). Other threatend species include Pavetta brachycalyx (EN), Garcinia afzelii and Monanthotaxis elegans (NE but provisionally VU, Onana, 2013). Ceropegia rhynchantha (VU), Afzelia africana (VU) and Cleome coeruleorosea are other species which may occur although not recorded. Despite many suggestions that the area harboured an important endemic flora, it has been little studied and there are few collections. It is possible that this flora is partly already extinct.

Habitat and geology

Unlike the spectacular volcanic (trachyte and rhyolite) necks and dykes of the Kapsiki peaks to the south, this part of the Mandara mountains is formed of uplifted ancient granitie (or granitic) rocks (Seymour, 2004; Thiéblemont et al., 2021). These rocks weather in the arid climate to porous, poorly developed and infertile soils, predominantly regosols, leptosols and luvisols (Yerima & Van Ranst, 2005. Some more fertile clays and other soil types are also present in alluvial areas and the landscape is much modified by terrace cultivation, crop rotation and livestock fertilisation (Sani et al., 2019; Seymour, 2004). There is a two-season climate with c. 1000-1500 mm precipitation per annum (WMO, 2022). Mean temperatures are from 15-30 °C (Seymour, 2004).
The original vegetation of the Mandara Mountains is believed to have been a form of Isoberlinia doko woodland but is now much degraded (Seymour, 2004). Species such as Vachellia nilotica, Faidherbia albida, Balanites aegyptiaca, Ziziphus spp., Crateva adansonii and Khaya senegalensis are common where trees survive and grasses dominate the herbaceous vegetation.

Conservation issues

The Mandara Plateau ecoregion is assessed by Seymour (2004) as crititcally threatened, having lost an estimated 98% of its natural habitat, the highest of any ecoregion in Africa or Madagascar.
Population density exceeds 300 people per km2 and the area has a long history of human occupation owing to the wetter climate and protective mountains (Seymour, 2004; Sani et al., 2019).
Terrace farming, grazing, burning and intense wood-gathering have transformed the landscape and remain the main threats. The continuing activity of the terrorist movement Boko Harem, which uses the mountains as a stronghold, limits the current potential for conservation action and surveying. However, surveying is vitally needed. Since the vegetation has never been well known it is hard to know what species may have been lost from the area, some perhaps narrow endemics.

Ecosystem services

The Mandara Mountains harbour rare wildlife with 319 birds and 84 mammals recorded, including Ruppel's Griffon (EN), Egyptian Vulture (EN) and Western Mountain Reedbuck (EN), and three near-endemic reptile species: Mount Lefo chameleo, Langheld's Skink and African wall gecko (Seymour, 2004). Gilbert et al. (2019) found that 50 species of woody plant had ethnobotanic uses in the local district of Merri.
The loss of natural vegetation is likely to have impacted the water-retention of the mountains, especially given the free draining mountain soils (Yerima & Van Ranst, 2005), leading to erosion, drought and flooding in the valleys.

Site assessor(s)

Bruce Murphy, Royal Botanic Gardens, Kew

IPA criterion A species

Species Qualifying sub-criterion ≥ 1% of global population ≥ 5% of national population 1 of 5 best sites nationally Entire global population Socio-economically important Abundance at site
Garcinia afzelii Engl. A(i) False False False False False
Pavetta brachycalyx Hiern A(i) False False False False False
Khaya senegalensis A.Juss. A(i) False True False False False
Euphorbia desmondii Keay & Milne-Redh. A(i) True True True False False
Vepris heterophylla (Engl.) Letouzey A(i) False False True False False

Garcinia afzelii Engl.

Qualifying sub-criterion:
A(i)
≥ 1% of global population:
False
≥ 5% of national population:
False
1 of 5 best sites nationally:
False
Entire global population:
False
Socio-economically important:
False
Abundance at site:

Pavetta brachycalyx Hiern

Qualifying sub-criterion:
A(i)
≥ 1% of global population:
False
≥ 5% of national population:
False
1 of 5 best sites nationally:
False
Entire global population:
False
Socio-economically important:
False
Abundance at site:

Khaya senegalensis A.Juss.

Qualifying sub-criterion:
A(i)
≥ 1% of global population:
False
≥ 5% of national population:
True
1 of 5 best sites nationally:
False
Entire global population:
False
Socio-economically important:
False
Abundance at site:

Euphorbia desmondii Keay & Milne-Redh.

Qualifying sub-criterion:
A(i)
≥ 1% of global population:
True
≥ 5% of national population:
True
1 of 5 best sites nationally:
True
Entire global population:
False
Socio-economically important:
False
Abundance at site:

Vepris heterophylla (Engl.) Letouzey

Qualifying sub-criterion:
A(i)
≥ 1% of global population:
False
≥ 5% of national population:
False
1 of 5 best sites nationally:
True
Entire global population:
False
Socio-economically important:
False
Abundance at site:

General site habitats

General site habitat Percent coverage Importance
Shrubland - Subtropical/Tropical High Altitude Shrubland No value

Shrubland - Subtropical/Tropical High Altitude Shrubland

Percent coverage:
No value
Importance:

Land use types

Land use type Percent coverage Importance
Harvesting of wild resources No value
Agriculture (pastoral) No value
Agriculture (arable) No value

Harvesting of wild resources

Percent coverage:
No value
Importance:

Agriculture (pastoral)

Percent coverage:
No value
Importance:

Agriculture (arable)

Percent coverage:
No value
Importance:

Threats

Threat Severity Timing
Agriculture & aquaculture - Annual & perennial non-timber crops - Small-holder farming High Ongoing - trend unknown
Agriculture & aquaculture - Livestock farming & ranching - Nomadic grazing High Ongoing - trend unknown
Natural system modifications - Fire & fire suppression - Increase in fire frequency/intensity High Ongoing - trend unknown
Biological resource use - Logging & wood harvesting High Ongoing - trend unknown
Human intrusions & disturbance - War, civil unrest & military exercises Medium Ongoing - trend unknown

Agriculture & aquaculture - Annual & perennial non-timber crops - Small-holder farming

Severity:
High
Timing:
Ongoing - trend unknown

Agriculture & aquaculture - Livestock farming & ranching - Nomadic grazing

Severity:
High
Timing:
Ongoing - trend unknown

Natural system modifications - Fire & fire suppression - Increase in fire frequency/intensity

Severity:
High
Timing:
Ongoing - trend unknown

Biological resource use - Logging & wood harvesting

Severity:
High
Timing:
Ongoing - trend unknown

Human intrusions & disturbance - War, civil unrest & military exercises

Severity:
Medium
Timing:
Ongoing - trend unknown

Bibliography

White, A.F., 1983

The vegetation of Africa. A descriptive memoir to accompany the UNESCO/AETFAT/UNSO vegetation map of Africa

Olson, D.M. et al., 2001

Terrestrial ecoregions of the world: a new map of life on earth

Bioscience, Vol 51, page(s) 3-938

Onana, J.M., 2011

Vascular Plants of Cameroon: Taxonomic Checklist. In: Flore Du Cameroon, Occasional Volume, IRAD-National Herbarium of Cameroon, Yaounde, 195.

Yerima, B. & Van Ranst, E., 2005

Major Soil Classification Systems Used in the Tropics: Soils of Cameroon

Thiéblemont D. (edit.) et al., 2021

Geological Map of Africa at 1:10 M scale, CGMW-BRGM 2016

Seymour, C., 2022

Mandara Plateau Ecoregion

Available online

Rivers, M.C., 2021

Euphorbia desmondii. The IUCN Red List of Threatened Species 2021: e.T165197393A165197765.

Available online

Sani, R., Ntoupka, M., Toua, V. & Ibrahima, A., 2019

Phytoecological valorization attributes of Mozogo-Gokoro National Park (Cameroon)

Environ Monit Assess, Vol 191(2), page(s) 79

Todou, G., Nnanga, J.F., Bayé-Niwah, C., Kamblaba, P., Froumsia, M. & Ibrahima A., 2019

Ethnobotanical study of indigenous woody plants in traditional agroforestry of the Sudano-Sahelianzone of Cameroon: case of Mandara Mountains

SSRG International Journal of Agriculture & Environmental Science, Vol 6(6), page(s) 1-8

Recommended citation

Bruce Murphy (2024) Tropical Important Plant Areas Explorer: Mount Opay (Cameroon). https://tipas.kew.org/site/mount-opay/ (Accessed on 27/07/2024)