| Location | Tanzania, Kilimanjaro |
| Central coordinates | 37o 20.00' East 3o 5.00' South |
| IBA criteria | A1, A2, A3 |
| Area | 166,100 ha |
| Altitude | 1,250 - 5,895m |
| Year of IBA assessment | 2001 |
Ornithological information See Box and Tables 2 and 3 for key species. Of relatively recent origin, the forest on Kilimanjaro holds few of the rarer species associated with the older forests of the Eastern Arc mountains. Cinnyricinclus femoralis is resident in forest on the southern and western slopes. The western slopes are important for the passage of Falco naumanni, with hundreds and possibly thousands of birds moving through, and for Circus macrourus, with several hundred birds thought to pass through. In addition, Ardeola idae is an irregular visitor to swamps and ponds at the foot of the mountain; Falco fasciinucha is known from two old sight records on the east of the mountain; Crex crex is known from four recent April/May records from the south-western foothills. Among the montane forest birds Bostrychia olivacea is notable as it has a restricted distribution and is rare wherever it occurs. Alpine species include Cercomela sordida and Nectarinia johnstoni, which are restricted to East Africa, and more widespread species such as Gypaetus barbatus and Tachymarptis melba. A range of birds more typical of coastal forest are found along the Sanya river including Telophorus quadricolor, Macrosphenus kretschmeri and Andropadus importunus. Permanent and seasonal swamps fed by the mountain provide breeding habitat for several uncommon species including Thalassornis leuconotus, Circus ranivorus, Porphyrio porphyrio and Gallinula angulata.
Site description Kilimanjaro is one of the largest isolated mountains in the world and is the highest in Africa, dominating the surrounding central plateau country. Mount Kilimanjaro National Park lies above the 2,700 m contour, which is virtually the upper altitudinal limit of forest. Montane forest occurs between 1,700 m and 2,800 m with a downward extension to 1,250 m in the south-west along the Sanya river. In the north there is an 8 km wide corridor of dry woodland linking the forest with bushland in the Longido Game Controlled Area (TZ074). In the east and south the lower slopes are densely cultivated, but in the drier west there are large estates and ranches with some remaining natural habitat. Plantations of exotic pines Pinus dominate the northern and north-western slopes.
| Species | Season | Period | Population estimate | Quality of estimate | IBA Criteria | IUCN Category |
|---|---|---|---|---|---|---|
| Lesser Kestrel Falco naumanni | passage | - | present [units unknown] | - | A1 | Least Concern |
| Pallid Harrier Circus macrourus | passage | - | present [units unknown] | - | A1 | Near Threatened |
| Mountain Buzzard Buteo oreophilus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Striped Flufftail Sarothrura affinis | resident | 2000 | unknown [units unknown] | - | A3 | Least Concern |
| Dusky Turtle-dove Streptopelia lugens | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Hartlaub's Turaco Tauraco hartlaubi | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Montane Nightjar Caprimulgus poliocephalus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Scarce Swift Schoutedenapus myoptilus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Nyanza Swift Apus niansae | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Bar-tailed Trogon Apaloderma vittatum | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Cinnamon-chested Bee-eater Merops oreobates | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Moustached Green-tinkerbird Pogoniulus leucomystax | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Grey Cuckooshrike Coracina caesia | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Hunter's Cisticola Cisticola hunteri | resident | 2000 | present [units unknown] | - | A2, A3 | Least Concern |
| Eastern Mountain Greenbul Andropadus nigriceps | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Stripe-cheeked Greenbul Andropadus milanjensis | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Bracken Warbler Bradypterus cinnamomeus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Mountain Flycatcher-warbler Chloropeta similis | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Brown Woodland-warbler Phylloscopus umbrovirens | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| African Hill Babbler Pseudoalcippe abyssinica | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Montane White-eye Zosterops poliogastrus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Sharpe's Starling Cinnyricinclus sharpii | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Abbott's Starling Cinnyricinclus femoralis | resident | 2000 | present [units unknown] | - | A1, A2, A3 | Vulnerable |
| Waller's Starling Onychognathus walleri | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Kenrick's Starling Poeoptera kenricki | resident | 2000 | present [units unknown] | - | A2, A3 | Least Concern |
| Abyssinian Ground-thrush Zoothera piaggiae | resident | 2000 | present [units unknown] | - | A3 | Not Recognised |
| White-starred Robin Pogonocichla stellata | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Rueppell's Robin-chat Cossypha semirufa | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Moorland Chat Cercomela sordida | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| White-eyed Slaty Flycatcher Dioptrornis fischeri | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Eastern Double-collared Sunbird Nectarinia mediocris | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Tacazze Sunbird Nectarinia tacazze | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Bronze Sunbird Nectarinia kilimensis | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Golden-winged Sunbird Nectarinia reichenowi | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Red-tufted Sunbird Nectarinia johnstoni | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Baglafecht Weaver Ploceus baglafecht | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Red-faced Crimson-wing Cryptospiza reichenovii | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Abyssinian Crimson-wing Cryptospiza salvadorii | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Swee Waxbill Estrilda melanotis | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Grey-faced Citril Serinus hypostictus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Streaky Seedeater Serinus striolatus | resident | 2000 | present [units unknown] | - | A3 | Not Recognised |
| Thick-billed Seedeater Serinus burtoni | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| Oriole Finch Linurgus olivaceus | resident | 2000 | present [units unknown] | - | A3 | Least Concern |
| IUCN habitat | Habitat detail | Extent (% of site) |
|---|---|---|
| Artificial landscapes (terrestrial) | 9% | |
| Shrubland | 17% | |
| Grassland | 21% | |
| Forest | 51% |
| Land-use | Extent (% of site) |
|---|---|
| agriculture | - |
| forestry | - |
| nature conservation and research | - |
| tourism/recreation | - |
| water management | - |
Other biodiversity An isolated population of elephant Loxodonta africana (EN) occurs. There are one endemic species of shrew, four endemic species and subspecies of butterfly, six endemic plants, and 12 endemic mosses and liverworts. Levels of endemism are highest in the moorland and alpine areas.
Management considerations Huge, regular fires are a key threat in the National Park. There is increasing evidence that montane forest has retreated downslope, by up to 8 km in some localities, as a result of continued burning at higher elevations. Most fires are started close to routes used by tourists. There is continued concern about habitat degradation and loss in the Forest Reserves and illegal cultivation, logging, grazing, unsustainable honey gathering, pole-cutting and collection of firewood. However, the greatest damage to forest in recent years has been the clearance of large areas of natural tree cover to create monocultures of exotic pines.
References Beck et al. (1986), Cordeiro (1993, 1994), Dowsett (1977), Greenway (1965), Lamprey (1965), Lusigi (1992), Moreau (1936, 1944), Moreau and Moreau (1939), Newmark (1991), Rundel et al. (1994), WCMC (1995), WWF/IUCN (1994–1997).
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Recommended citation BirdLife International (2013) Important Bird Areas factsheet: Mount Kilimanjaro. Downloaded from http://www.birdlife.org on 23/05/2013
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