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TWONGO, T.K.
National Agricultural Research Organisation (NARO),
Fisheries Resources Research Institute (FIRRI), P.O. Box 343, Jinja,
Uganda. E-mail: firi@infocom.co.ug
Distribution of water hyacinth in Uganda, its
control and impacts of control measures
Water hyacinth invaded Lake Victoria from Rwanda via River Kagera
during the second half of the 1980's. Prevailing winds and associated
currents facilitated weed distribution along the northwestern shores
of the lake while sheltered bays and inlets favoured establishment.
Infestation of water hyacinth in Lake Kyoga, Uganda occurred at
about the same time, from an unknown source. Weed distribution was
completed by 1990, facilitated mainly by the general east- west
water flow regime. Distribution and establishment of water hyacinth
along lower Victoria Nile, the northern shores of Lake Albert and
the Albert Nile were completed by 1991, aided by down-river transport.
Weed establishment occurred in zones sheltered from direct river
currents and offshore winds. Fringes of papyrus, bulrush (Typha
sp) and hippograss (Vossia cuspidata) were identified
as indicator macrophytes of suitable environments for water hyacinth
establishment. In Uganda, striking weed redistribution was achieved
on Lake Victoria through annual cross-lake migrations. Similarly,
proliferation and constant translocation of water hyacinth biomass
down rivers, Kagera and the Nile, are important channels of weed
redistribution in Lake Victoria and the Nile system.
Water hyacinth control was effected mainly by biological control
with Neochetina weevils, environmental stress, and natural ecological
succession with native macrophytes dominated by hippograss. Physical
harvesting was used to alleviate weed burden at the small landing
beaches and at key economic installations. Adverse ecological impacts
of water hyacinth were mostly due to smothering and displacement
of biodiversity and various inshore biological processes. Major
impacts of control measures included prolonged depression of dissolved
oxygen at the lake bottom, suspected loading of sediments with phosphorus,
and a temporary boost in fishery production, in bays where massive
sinking of the weed occurred due to stress by biological control
and environmental factors.
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