Summary
Lake Victoria, one of the largest freshwater bodies
of the world, is shared by three countries: Kenya, Tanzania and Uganda.
The lake sustains important fisheries and is used for commercial navigation.
The Owen Falls dam at its outlet allows for the use of regulated outflow
for hydropower generation. Lake Victoria is one of the sources of the Nile,
a river whose waters are heavily committed downstream. In recent years,
environmental challenges have beset the Lake: the introduction of an exotic
fish, the Nile perch, upset the ecological balance with harm for biodiversity,
and a water hyacinth invasion has caused a host of problems. International
cooperation around the Lake has a long history because of its significance
as a source of the Nile and a major data collection and modeling effort
took place in the 1960s and 70s. More recently, the countries that share
the Lake have joined with the international community in efforts to manage
and preserve its water resources, fisheries, and environment.
Physical and political background
Lake Victoria (see Figure 1) has a surface area of about
69,000 km2 shared by three countries, with a land drainage area
of slightly over 181,000 km2 in 5 countries (Table 1). The mean
depth is of about 40 m with a recorded maximum depth of 84 m and the volume
of water stored is estimated at about 2,760 km3.
Table 1: Lake Victoria surface area, shoreline and
basin area per country
Country | Lake surface area | Shoreline | Tributary | basin | ||
km2 | % | km | % | km2 | % | |
Kenya | 4,113 | 6 | 550 | 17 | 38,913 | 21.5 |
Tanzania | 33,756 | 49 | 1150 | 33 | 79,570 | 44 |
Uganda | 31,001 | 45 | 1750 | 50 | 28,857 | 15.9 |
Rwanda | 0 | 0 | 0 | 0 | 20,550 | 11.4 |
Burundi | 0 | 0 | 0 | 0 | 13,060 | 7.2 |
Total | 68,870 | 100 | 3450 | 100 | 180,950 | 100 |
The gross economic product in the lake catchment is of
about US$ 3 to 4 million annually and supports an estimated population
of 25 million people at average incomes in the range of US$ 90 to 270 per
annum (1). Population density in the Lake basin is above the national average
in all countries and the populations of the riparian communities grow at
rates that are among the highest in the world.
Lake Victoria moved into the focus of attention in the 19th century, when it was identified as one of the sources of the Nile. Because it has a control structure for a large hydropower plant at its outlet in Owen Falls, the Lake is classified as a very large reservoir. However, hydrologically the Lake behaves like a closed system, as can be seen in the water balance of Table 2. It takes about 73 years for a volume of water equivalent to the Lake to flow out of it Historically, somewhat above average rainfall in the early 1960s resulted in a sudden rise in water level of 2 m and extensive shore flooding. Since then, lake levels have receded to historic averages. Limnologically, the Lake is monomictic and primary productivity is high.
Figure 1: Lake Victoria and its catchment on Kenya, Tanzania and Uganda.
Table 2: Lake Victoria annual water balance 1965 -
1990
Water balance component | Volume | Lake level equivalent |
(km3) | (m) | |
Lake rainfall | 125 | 1.81 |
Lake evaporation | 110 | -1.6 |
Lake net rainfall | 14,5 | 0.21 |
Catchment rainfall | 293 | n.a. |
Catchment evaporation | 270 | n.a. |
Inflow from catchment | 23 | 0.34 |
Net basin supply | 37,5 | 0.55 |
Outflow (Owen Falls) | 38 | -0.57 |
Water quality
The Secchi transparency index has declined from 5 meters
in the 1930s to less than one meter in the 1990s. Pollution pressures are
increasing and pollution impact by municipal and industrial discharges
is visible in some of the rivers feeding the Lake and along the shoreline,
such as the shallow Winam Gulf (Kisumu) and near Mwanza and Kampala. Among
the sources of pollution are a number of basic industries such as breweries,
tanning, fish processing, agroprocessing and abattoirs. Small scale gold
mining is increasing in parts of the Tanzanian catchment, leading to contamination
of the waterways by mercury.
Increased nutrient flows are coming mostly from rural areas. Fertilizer use in the farms of the region is limited and therefore it may be supposed that the nutrients are released from soil particles washed off the land by erosion, from burning wood-fuels, and from human and animal waste from the areas surrounding the Lake. From the urban areas, the main source is untreated sewage (2).
The increased inflow of nutrients into the Lake is resulting
in eutrophication. Phosphorus and nitrogen concentrations have risen and
algal growth has increased five-fold since the 1960s. A shift of algal
flora composition towards blue-green algae is causing deoxygenation of
water, health problems for humans and animals drawing water from the Lake,
clogging of water intake filters and increased treatment costs for urban
centers. Deepwater species have sharply declined and periodic upwelling
of hypoxic water has caused massive fish kills.
Fisheries
The commercial fish catch is dominated by Nile Perch
(60%), an introduced species that has expanded rapidly since 1978. The
size of fisheries, which was of only some 100,000 tons in 1978, exploded
with the introduction of the Nile Perch. Lake Victoria fisheries yields
in recent years have been estimated at 300,000 to 500,000 tons per year.
Sustainability of fisheries is threatened by overfishing, pollution and
the ecological instability resulting from the introduction of the Nile
Perch (1).
The need for fisheries collaboration in Lake Victoria
was realized already in 1928. More recently, the three countries collaborated
through the FAO Committee for Inland Fisheries of Africa (CIFA) Sub-Committee
for Lake Victoria. A Convention for the Establishment of the Lake Victoria
Fisheries Organization (LVFO), drafted with FAO assistance, was signed
by all three countries in 1994. The LFVO will promote better management
of fisheries on the Lake, coordinate fisheries management with conservation
and use of other Lake resources, collaborate with existing bodies and programs
dealing with Lake management, coordinate fisheries extension, advise on
introduction of non-indigenous animals or plants into the Lake, and disseminate
information on Lake Victoria. The newly established LVFO is currently supported
by the European Union through the Lake Victoria Fisheries Research project.
Water hyacinth
The appearance of the water hyacinth (Eichhornia crassipes)
in Ugandan waters of Lake Victoria was first reported in 1988. The source
of infestation appears to be the Kagera river, the main tributary to the
Lake, which drains also parts of Rwanda and Burundi. Owing to the predominance
of southerly winds, water hyacinth is particularly dense in Ugandan waters
on the northern shore, and the area between Entebbe and the Kenyan border
has large floating mats. Water hyacinth interferes with fishing operations
and commercial transportation services, increases the cost of water supply
from the Lake, threatens the intakes at the Owen Falls power station, reduces
fish in the Lake through de-oxygenation, and provides a preferred habitat
for bilharzia hosts and vector mosquitoes for malaria (1).
FAO has provided assistance to the countries concerned
in the assessment and in the establishment of the capacity to control water
hyacinth in Lake Victoria. The control strategy is based on a biological
control programme that relies on two weevil species that have been found
effective world-wide. The main elements of the biological control programme
are the establishment of mass rearing capacity, a coordinated field release
programme, and monitoring performance. Biological control is not expected
to overcome the problem totally and immediately. Thus, the control programme
also relies on mechanical removal methods and on chemical interventions
in restricted areas.
Water resources monitoring and management
All riparian countries have plans to use its waters for various purposes. Knowledge and understanding of the water regime in the Lake basin is a prerequisite for improving the capacity to sensibly manage the resource. Data collection efforts carried out in the 1960s and 70s under the WMO/UNDP Hydrometeorological Survey project provided a valuable crop of data but were interrupted owing to war events in the region. Currently, the need to catch up with the most basic infrastructure for water management is addressed through the regional FAO/Japan "Lake Victoria Water Resources (LVWR)" project.
The LVWR project has initiated the establishment of a
sustainable skeleton network of rain gauges and river gauges for Lake management.
Ground data will be integrated with remote sensing data in a geographically
referenced (GIS) database. The database will be used through a water resources
simulation model for spatial estimation of the rainfall regime, rainfall-runoff
and river flow simulation, and a control/decision support system (DSS)
for reservoir operation and water management. The DSS will assist the riparian
countries in formulating a coordinated and mutually agreed upon management
strategy for the Lake, and promote the institutional process within which
the three countries will continue cooperation and interaction in Lake management.
A variety of options have been identified for configuring
a tripartite institution for regional cooperation in the environmental
management of the lake Victoria water resources and of its catchment (3).
As the most effective approach, the Steering Committee of the LVWR project
has undertaken steps to bring to the attention of the Permanent Tripartite
Commission for Cooperation between Kenya, Tanzania and Uganda the need
to incorporate representatives of the water administration of the three
member states in any arrangement for tripartite cooperation in the water
resources management of the Lake Victoria basin under the aegis of the
Commission.
Environmental management
The natural resources of the Lake basin are used to obtain
food, shelter and energy, to secure residential and industrial water supply
and transport needs, for irrigation and to dispose of human, agricultural
and industrial waste. In recent decades, with growing population and development,
the multiple activities in the Lake basin have increasingly come into conflict
and the Lake ecosystem has undergone substantial changes rendering the
Lake environment unstable.
The Lake Victoria Environmental Management Project (LVEMP)
is a comprehensive programme aimed at rehabilitation of the lake ecosystems
for the benefit of the people in the catchment and the national economies
of which they are part. The objectives of the programme are to:
(a) maximize the sustainable benefits to riparian communities from using resources within the basin to generate food, employment and income, supply safe water, and sustain a disease-free environment, and
(b) conserve biodiversity and genetic resources (World Bank, 1996).
The first phase of the project, with funding at the level
of US$ 80 million by the Global Environment Facility (GEF), the World Bank,
the three countries concerned and several donors, deals with fisheries
management, water hyacinth management and control, management of lake pollution
and water quality, management of land use in the catchment, management
of wetlands and support for institutions for lake-wide research and management
and pollution disaster contingency planning. Implementation of the LVEMP
was initiated in mid-1997 and the first phase is to last five years (1).
Conclusions
Lake Victoria, for a long time seen mainly as a convenient
reservoir for downstream water users, is now percveived by its riparian
countries as an important resource that requires rational management to
protect it from pollution and degradation. Kenya, Tanzania and Uganda have
joined to assess the resources and the problems of the Lake, to develop
management tools and to establish adequate institutions and capacity. Benefits
will accrue to the population in the catchment, to the riparian countries
and to the global community.
References
(1) World Bank: Staff Appraisal Report for the Lake
Victoria Environmental Management Project, Report No. 15429-AFR, Washington,
1996.
(2) Bullock, A. et al.: Report on LVEMP tasks 11,
16 and 17, FAO, 1995.
(3) Burchi, S.: Institutional Options (revisited)
for Lake Victoria Cooperation, Proceedings of the Second Regional Workshop
of the LVWR Project, FAO/LVWR, Kampala, 1997.