KE061
Lake Ol' Bolossat This is an IBA in Danger! 


Site description (2007 baseline):

Site location and context
Lake Ol' Bolossat, Central Province's only natural lake, is an internal drainage basin whose swamps have a high salt content possibly due to high evaporation rates and partly to the nature of sediments that constitute the area (Krhoda 1992). The lake is situated in the valley between the northwestern slopes of Aberdares Mountains and Dundori Ridge which are the main catchments. The altitude ranges from 2,340 - 2,400 meters above sea level, receiving an average precipitation of 975 - 1,100 mm pa. The Lake covers an area of 43.3 sq.km. of which open water covers about 4 sq.km. This drainage basin, Ewaso Ngiro North Basin covering 210,226 sq.km., is Kenya's largest. It offers a variety of habitats ranging from open water through floating marsh and swamps, open grasslands and riverine forests along rivers and springs that feed the lake.

Key biodiversity
Lake Ol’ Bolossat holds a wealth of bird species that would attract bird watchers in the tourism industry. A total of 49 species were recorded in a survey by Wamiti et al in 2007. The Lake is known to be important for Palearctic migrant waterbirds. During the 2007 survey, 17 waterbird species that are listed by the African-Eurasian Waterbird Agreement (Ng'weno et al 1999) were recorded. This emphasizes the importance of protecting the wetland for, among other reasons, being close the Great Rift Valley, one of Kenya's important migration flyways, thus offering a suitable site for feeding and resting, and probably as a wintering ground for the Palaearctic migrants. The area around Lake Ol’ Bolossat holds a significant area (c.39 sq.km.) of unique montane grasslands. The highland grasslands of central Kenya contain a suite of restricted-range bird species, forming part of Kenyan Mountains Endemic Bird Area (Stattersfield et al 1998). These grasslands have received virtually no conservation attention from the authorities, are largely unprotected and are vanishing at an alarming rate (Fanshawe & Bennun 1991, Bennun & Njoroge 2001) despite being habitats for globally-threatened bird species as well as other biodiversity. Sharpe's Longclaw Macronyx sharpei, a globally-threatened and Kenyan high-altitude grassland endemic bird (BirdLife International 2000, 2006, Muchai et al 2002, Muchai 1997), has been recorded in the area’s open grasslands during a waterfowl census (Mungai & Manegene 1998) and in early 2007. Suitable habitat for Sharpe's Longclaw in Kenya is found in Kinangop, Mau Narok & Molo grasslands, and Uasin Gishu plateau. Previous records reports this species as having been recorded from the north-west slopes of Mt. Kenya and the moorlands of Aberdares Mountains although there have been no recent records in these two sites (Zimmerman et al 1996). The presence of Sharpe's Longclaw has been confirmed at Lake Ol' Bolossat, which extends the species' current known distribution and further suggests that it might have had a wider distribution than historically known. Jackson's Widowbird Euplectes jacksoni, also a restricted-range species and described as near-threatened (NT) by BirdLife International (2000), was also recorded in private farms. There has been scarce and unpublished information on sightings and status of these two species, or that of their grassland habitat at the site. Long-tailed Widowbird E. progne, a regionally-threatened species, was also observed. Hunter's Cisticola Cisticola hunteri (Least Concern) was recorded mainly from bushes in the farmlands. The Lake's open water and swamps are home to a number of waterbirds. Interesting species observed includes African Marsh Harrier, Purple Swamphen, Black-bellied Bustard and Capped Wheatear. The most abundant species recorded in the 2007 survey were Long-tailed Widowbird (114), Red-capped Lark (93) and Grassland Pipit (89).

Non-bird biodiversity: Hippopotamuses, estimated at over 200 individuals, which graze overnight.



Habitat and land use
Grassland/pasture, cultivation, exotic tree plantations, settlements and water reservoirs were identified. Cultivation covers less proportion, whereas grasslands covered most of the area. Plantations of Eucalyptus are now taking up most of the area to drain the wetland and due to the high demand of industrial poles. Wheat and maize are also cultivated but their full potential in the area has not been established. However, animals are grazed at high densities both on the eastern and western sides of the grasslands around the Lake. Due to water logging in the basin, the settled land is not even suitable for agriculture. This leaves it only viable for conservation and recreation.

Pressure/threats to key biodiversity
The main threat facing the wetland, including the riparian land where the tussock grasslands are found, are human encroachment and settlement. Other human activities affecting the site are quarrying (rock harvesting) and farming. Lack of a legal framework is the main problem inhibiting rehabilitation of land and implementation of conservation efforts (Kariuki 2007). There has been a fast increase in intensive agricultural production along inlets and general lake area that is likely to affect water levels in the wetland due to water abstraction and can also lead to siltation. The rate of water reduction and actual loss at Lake Ol Bolossat is unknown. Afforestation along streams and rivers with indigenous tree species and appropriate agro-forestry trees and shrubs in the farms is needed as a sustainable water and soil conservation measure. It was observed that some parts of the open plains had been ploughed earlier and later abandoned. Recovery of native vegetation cover has been futile due to overgrazing. There is also a high livestock (cattle, goats, sheep and donkeys) stocking rates on the plains. This represents the case of a tragedy of the commons where people stock high numbers of livestock, which the grasslands generally seem unable to accommodate. This high stocking rate reduces tussock density and grass cover that is suitable for Sharpe's Longclaw conservation. It also has a potential of exposing topsoil to wind and water erosion. At some points, serious soil erosion was observed at the lake shores. A management plan for Lake Ol’ Bolossat for the years 2003-2008 was never implemented. The stakeholders, including Kenya Wetlands Forum, East African Wild Life Society, Kenya Wildlife Service, County Council of Nyandarua, NEMA, Lake Ol’ Bolossat Environmental Conservation Network, and several Government Departments, to mention but a few, should work to revise and implement the stalled 2003-2008 management plan. According to the plan, the main threats facing this fragile ecosystem come from land use practices in the area, primarily urban development, small and large-scale intensive agriculture, ranching, forestry and wildlife conservation. These activities result in deforestation, disruption of the hydrological balance, pollution, waste disposal, land degradation, soil erosion and siltation. During the 2007 survey, a high stocking rate of livestock grazing on the plains near human settlements was noted. Overgrazing by livestock seems to pose a major threat to grassland habitat quality. Overgrazing is further exacerbated by the presence of Hippopotamuses, estimated at over 200 individuals, which graze at night.

Land ownership
Unprotected.

Acknowledgements
The British Ornithologists’ Union (BOU) for providing funds for research. The Wetlands Programme and Office of the Deputy Director Biodiversity Research & Monitoring at Kenya Wildlife Service headquarters. The Chairman, Lake Ol Bolossat Conservation Network, Mr. Joseph Mbugua, for logistics. Field assistants and community local guides Teresia Maina and Paul Ndegwa, and Catherine Wambui of Kenya Forest Service based at South Marmanet Forest, for their field work facilitation


Recommended citation
BirdLife International (2024) Important Bird Area factsheet: Lake Ol' Bolossat. Downloaded from https://datazone.birdlife.org/site/factsheet/lake-ol-bolossat-iba-kenya on 29/02/2024.