Mount Morungole

Morungole Central Forest Reserve

UGATIPA38
Mount Morungole

Country: Uganda

Administrative region: Northern (Region)

Central co-ordinates: 34.83670 N, 34.01511 E

Area: 342km²

Qualifying IPA Criteria

A(i)Site contains one or more globally threatened species, A(iv)Site contains one or more range restricted endemic species that are potentially threatened, B(ii)Site contains an exceptional number of species of high conservation importance

IPA assessment rationale

Morungole CFR qualifies as an IPA under criterion A(i) triggered by the presence of the Endangered Aloe lukeana for which this is the most important site globally, and the Vulnerable Aloe tweedieae. It also qualifies under criterion A(iv) due to the presence of a population of the range-restricted Aloe canarina, which is currently assessed as Data Deficient but is likely to be threatened. Lastly, it is one of Uganda's top 13 richest sites for endemic plant species, triggering criterion B(ii).

Site description

Morungole Central Forest Reserve (CFR) is located in between Karenga and Kaabong districts, north-eastern Uganda. The reserve lies approximately 35 km north of Kaabong town and forms part of the south-east boundary of Kidepo National Park (Davenport & Howard 1996). The mountain top is home to a minority indigenous community of the “Ik” people who have a unique culture different from that of the neighbouring Dodoth Karamojong.

Botanical significance

Whilst the flora in Morungole CFR is not especially diverse, it is characterised by a reasonable number of rare and/or restricted-range species of which some are of conservation importance. A total of 185 tree and shrub species were recorded in this reserve (Lwanga 1996). The botanical significance of this IPA is likely to increase with additional surveys of other plant lifeforms. Nonetheless, it is the principal site globally and type locality for the Endangered Aloe lukeana; a montane species occurring at 2300-2750 m in elevation on grassland with many herbs on rocky slopes, which is abundant on the upper reaches of Mt Morungole (Cole 2015; Cole & Forrest 2017; Richards et al. 2022). This taxon has otherwise also been recorded on the South Sudan side of the Imatong Mountains. So far, there is no documented evidence on the use of this species for medicinal purposes (Anywar et al. 2022).

Popluations of two further rare Aloe, A. tweedieae (VU) and A. canarina (DD), have recently been discovered on the foothills of Mt Morungole in the extreme southeast of the CFR (Cole 2015; T. Cole, pers. comm. 2023). Aloe tweedieae was noted to be common on rock outcrops and open grassland on the road north of Kaabong whilst A. canarina was noted to be occasional. This latter species is highly range-restricted and uncommon and is facing increased threats from tree cutting for firewood and increased frequency of burning to clear dried grass within its Ugandan range (Cole & Forrest 2017), hence the species is likely to be reassessed as globally threatened in the future. Plumptre et al. (2018) designated Morungole as a Key Biodiversity Area (KBA) on the basis of Aloe wrefordii, which has recently been reassessed as Endangered (Richards et al. in press) but this record is believed to be erroneous. This IPA contains Dry Afromontane Forest which is a Vulnerable (and highly range-restricted) habitat in Uganda but it does not trigger IPA status as the area of forest is not large enough (only c. 5 km2, which is 2% of national resource and outside the top five).

Habitat and geology

The vegetation in this IPA may be broadly classified as dry Combretum savannah with Juniperus-Podocarpus dry montane forest at higher elevations, and a high altitude forest/savannah mosaic. Areas adjacent to the peak of Mt Morungole are marked by Juniperus procera, low growing Protea gaguedi, and shrubs, ferns and grass species amongst exposed rock. Thomas (1943) cited by Cole (2015) described the area as "shrubby moorland grading into shrubby grassland at the summit. The Juniperus forest is very luxuriant high on the mountain, with copious mosses and lichen (Usnea longissima) and Cole (2015) noted that in some protected spots, Aloe lukeana and the succulent herb Aeonium leucoblepharum grow amidst orchids, mosses, lichen and other epiphytes high up into the branches of the juniper trees.

Mt. Morungole’s origin dates to the Mesozoic and Cenozoic eras associated with volcanic eruptions. Thus, it is an extinct volcano (Cheriberi & Yee 2022). Whilst stoney litho soils occur along the up-warped surface of Mt. Morungole, the other soil types include ferralytic, vertigos and ferruginous tropical soils. Ferralitic soils are in more advanced stages, their productivity depending on favorable rainfall, and adequate depth (UNDP 2014).

The area has a dry savanna semi-arid climate characterized by an intense hot, dry season lasting from November to March each year, with whirlwinds and dust storms. The rainy season is usually from April to August with an annual rainfall of 500–800 mm, with rains erratically distributed. The daily temperatures range from 20°C to 32°C degrees; relative humidity can reach 60% between June and July (UNDP 2014).

Conservation issues

Mount Morungole was designated as CFR in 1948. Some of the northern parts of the Reserve also fall within the boundary of Kidepo National Park. Mt Morongole has been encroached to some extent up to the peak (Rugadya et al. 2010) by the Ik communities who live at various altitudes on the mountain, in settlements referred to as “manyatta” and have associated areas of cultivation of crops such as cassava in the fertile montane valleys (Cole 2015; Richards et al. 2022). There are indiscriminate and uncontrolled seasonal fires on Mt. Morungole but the Aloe lukeana plants are not killed and regeneration after fire is evident from numerous seedlings observed (Cole 2015).

Ecosystem services

The Ik community living on Mt. Morungole obtain many products from this IPA. These include firewood, construction materials, edible plants, medicinal plants, craft materials among others. Morungole CFR, together with the Nyangea-Napore and Zulia hill ranges, is the source of most rivers in Karamoja region such as the Nalakas and Kidepo rivers (MTWA & UWA 2012). Mount Morungole provides scenic views of the surrounding areas as far as neighbouring Kenya and Sudan, thus offers a great opportunity for the local community to engage in tourism activities as guides and porters. It is also an ideal site for mountain hiking experience (MWTA & UWA 2012).

Site assessor(s)

Assessed by:

Samuel Ojelel, Makerere University Herbarium

James Kalema, Makerere University Herbarium

Iain Darbyshire, Royal Botanic Gardens, Kew

Sophie Richards, Royal Botanic Gardens, Kew

Date of first assessment: 16th Aug 2024

Reviewed by:

Charles Tumwesigye, Uganda Wildlife Authority

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
Aloe lukeana T.C.Cole A(i) True True True False False Abundant
Aloe canarina S.Carter A(iv) True True True False False Scarce
Aloe tweedieae Christian A(i) True True True False False Scarce

Aloe lukeana T.C.Cole

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:
Abundant

Aloe canarina S.Carter

Qualifying sub-criterion:
A(iv)
≥ 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:
Scarce

Aloe tweedieae Christian

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:
Scarce

IPA criterion C qualifying habitats

Habitat Qualifying sub-criterion ≥ 5% of national resource ≥ 10% of national resource 1 of 5 best sites nationally Areal coverage at site
Afromontane dry forest (CR) C(iii) False False False 4.96
Dry Combretum wooded grassland (VU) C(iii) False False False 233

Afromontane dry forest (CR)

Qualifying sub-criterion:
C(iii)
≥ 5% of national resource:
False
≥ 10% of national resource:
False
Areal coverage at site:
4.96

Dry Combretum wooded grassland (VU)

Qualifying sub-criterion:
C(iii)
≥ 5% of national resource:
False
≥ 10% of national resource:
False
Areal coverage at site:
233

General site habitats

General site habitat Percent coverage Importance
Forest - Subtropical/Tropical Dry Forest 35 Major
Savanna - Dry Savanna 55 Major
Grassland - Subtropical/Tropical High Altitude Grassland No value Minor
Rocky Areas - Rocky Areas [e.g. inland cliffs, mountain peaks] No value Minor

Forest - Subtropical/Tropical Dry Forest

Percent coverage:
35
Importance:
Major

Savanna - Dry Savanna

Percent coverage:
55
Importance:
Major

Grassland - Subtropical/Tropical High Altitude Grassland

Percent coverage:
No value
Importance:
Minor

Rocky Areas - Rocky Areas [e.g. inland cliffs, mountain peaks]

Percent coverage:
No value
Importance:
Minor

Land use types

Land use type Percent coverage Importance
Nature conservation 50 Major
Forestry No value Minor
Tourism / Recreation No value Minor
Agriculture (arable) No value Minor

Nature conservation

Percent coverage:
50
Importance:
Major

Forestry

Percent coverage:
No value
Importance:
Minor

Tourism / Recreation

Percent coverage:
No value
Importance:
Minor

Agriculture (arable)

Percent coverage:
No value
Importance:
Minor

Threats

Threat Severity Timing
Agriculture & aquaculture - Annual & perennial non-timber crops - Shifting agriculture Low Ongoing - increasing
Biological resource use - Logging & wood harvesting - Intentional use: large scale (species being assessed is the target) [harvest] Low Ongoing - increasing
Agriculture & aquaculture - Livestock farming & ranching - Small-holder grazing, ranching or farming Medium Ongoing - increasing
Natural system modifications - Fire & fire suppression - Increase in fire frequency/intensity Medium Ongoing - stable
Residential & commercial development - Housing & urban areas Low Ongoing - increasing

Agriculture & aquaculture - Annual & perennial non-timber crops - Shifting agriculture

Severity:
Low
Timing:
Ongoing - increasing

Biological resource use - Logging & wood harvesting - Intentional use: large scale (species being assessed is the target) [harvest]

Severity:
Low
Timing:
Ongoing - increasing

Agriculture & aquaculture - Livestock farming & ranching - Small-holder grazing, ranching or farming

Severity:
Medium
Timing:
Ongoing - increasing

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

Severity:
Medium
Timing:
Ongoing - stable

Residential & commercial development - Housing & urban areas

Severity:
Low
Timing:
Ongoing - increasing

Protected areas

Protected area name Protected area type Relationship with IPA Areal overlap
Morungole Central Forest Reserve Forest Reserve (conservation) protected/conservation area matches IPA 342
Kidepo Valley National Park National Park protected/conservation area overlaps with IPA 2

Morungole Central Forest Reserve

Protected area type:
Forest Reserve (conservation)
Relationship with IPA:
protected/conservation area matches IPA
Areal overlap:
342

Kidepo Valley National Park

Protected area type:
National Park
Relationship with IPA:
protected/conservation area overlaps with IPA
Areal overlap:
2

Management type

Management type Description Year started Year finished
No management plan in place No value No value

No management plan in place

Year started:
No value
Year finished:
No value

Bibliography

Plumptre, A. J., Ayebare, S., Behangana, M., Forrest, T. G., Hatanga, P., Kabuye, C., Kirunda, B., Kityo, R., Mugabe, H., Namaganda, M., Nampindo, S., Nangendo, G., Nkuutu, D. N., Pomeroy, D., Tushabe, H. & Prinsloo, S., 2019

Conservation of vertebrates and plants in Uganda: Identifying Key Biodiversity Areas and other sites of national importance

Conservation Science and Practice, Vol 1, page(s) 1-12 Available online

Cole, T., & Forrest, T., 2017

Aloes of Uganda: A field guide

UWA, 2012

Kidepo Valley National Park General Management Plan 2012-2022

Thomas, A. S., 1943

The Vegetation of the Karamoja District, Uganda: An Illustration of Biological Factors in Tropical Ecology

The Journal of Ecology, Vol 31, page(s) 149-177 Available online

Cole, T. C., 2015

Aloe lukeana: A New, Caulescent Aloe from Uganda

Cactus and Succulent Journal, Vol 87, page(s) 152-159 Available online

Anywar, G., Tugume, P. & Kakudidi, E. K., 2021

A review of Aloe species used in traditional medicine in East Africa

South African Journal of Botany, Vol 147, page(s) 1027-1041

Lwanga, J., 1996

Trees and Shrubs. In: Davenport, T., Howard, P. & Matthews, R. (eds), Kisangani Forest Reserve. Biodiversity Report

Cheriberi, D., & Yee, E., 2022

Preliminary Seismic Hazard Analyses for the Ugandan Region.

Applied Sciences,, Vol 12(2), page(s) 598

Davenport, T. & Howard, P., 1996

Morungole, Timu and Lwala Forest Reserves Biodiversity Report

Rugadya, M. A., Kamusiime, H., & Nsamba-Gayiiya, E.,

Tenure in mystery. Status of land under wildlife, forestry and mining concessions in Karamoja Region, Uganda, Kampala: Associates Research Uganda, with support from TROCAIRE Uganda and Oxfam GB

Available online

UNDP, 2014

KARAMOJA Kaabong district Hazard, Risk and Vulnerability Profie

Available online

Recommended citation

Samuel Ojelel, James Kalema, Iain Darbyshire, Sophie Richards (2025) Tropical Important Plant Areas Explorer: Mount Morungole (Uganda). https://tipas.kew.org/site/mount-morungole/ (Accessed on 14/05/2025)