Lake Nakuru Experience and Lessons Learned Brief Eric O. Odada*, Department of Geology, University of Nairobi, Nairobi, Kenya,
[email protected] Jackson Raini, World Wildlife Fund for Nature, Nakuru, Kenya Robert Ndetei, Wetland Programme, Kenya Wildlife Service, Kitengela, Kenya * Corresponding author 1. Introduction also decreased markedly (Vareschi 1978; Tuite 1979). The birds declined at Lake Nakuru, for example, from over one Lake Nakuru (Figure 1) is one of several shallow, alkaline-saline million to a few thousand after the salinity rose about 25% (20 lakes lying in closed hydrologic basins in the eastern African to 25 g/L between September 1973 to March 1974; Vareschi Rift Valley that stretches from northern Tanzania through 1982). The phytoplankton abundance also declined, with the Kenya to Ethiopia (Livingstone and Melack 1984). Typical of species switching to those too small for the fl amingoes to fi lter shallow, saline lakes around the world, climatic variations from the water. Although the sensitivity of these ecosystems have caused large changes in its depth and salinity on annual, to modest changes in salinity has been demonstrated, the decadal and longer time scales, with major consequences for underlying mechanisms for the multiple responses could only the lake’s ecology. Daily fl uctuations in heating and cooling be surmised (Melack 1988). have resulted in strong cycles of stratifi cation and mixing (Melack and Kilham 1974). High insolation and adequate The Lake Nakuru catchment basin is a closed drainage system supply of nutrients usually support abundant phytoplankton of 1,800 km2. The Menengai Crater (8,060-2,040 m asl) lies to (Peters and MacIntyre 1976; Melack et al.