Abstract:
Between 2000 and 2005 water quality and limnological
studies were carried
out in Lake Victoria in order to establish the eutrophication effects on ecosystem health.
Comparison between littoral and pelagic areas of the lake showed marked spatial and
temporal differences between and within the zones.
Nitrate
nitrogen (NO
3
-
N) and phosphate phosphorus (PO
4
-
P) concentrations
ranged between 16.2
-
87.9 μg/l and 39.6
-
92 μg/l respectively and were both higher in
the northeast. Silica (SiO
2
-
Si) concentrations ranged between 0.525 and 0.902 mg/l and
the values were
higher in the northeast and southwest compared to mid
-
lake stations.
Nyanza Gulf had lower PO
4
-
P concentrations (16.2 to 21.1μg/l) than the Mwanza and
Napoleon Gulfs (54.8 to 68.7μg/l) but registered higher SiO
2
-
Si concentrations (4.5 to 5.2
mg/l) than th
e other two gulfs.
NO
3
-
N concentration in the gulfs ranged between 25 and 93
μg/l with Napoleon Gulf having higher values than the other two gulfs. Total phosphorus
(TP) in the pelagic waters ranged between 0.078 and 0.10 mg/l and total nitrogen (TN)
range
d between 0.53 and 0.83 mg/l. The TN:TP ratio
(<20)
in the main lake indicate
d
that
phytoplankton growth in the lake may be nitrogen
-
deficient
; a situation favoring
dominance of nitrogen fixing Cyanobacteria. This low TN:TP ratio is probably associated
wit
h the increased phosphorus loading and selective nitrogen loss through denitrification
aqs well as
enhanced recycling of P associated with increased anoxic conditions in the
deep pelag
ic waters. Comparison with Tall
ing’s 1961 values, SiO
2
-
Si concentrations
in the
lake have generally decreased by a factor of 3 and up to 8 at the
Talling’s
historical
station of Bugaia (UP2). Chlorophyll a concentrations in the pelagic areas ranged
between 3.6 and 11.7 μg/l and were generally higher in the littoral than to the
pelagic areas. The phytoplankton community was dominated by Cyanobacteria (>50%) especially
the species Microcystis, Anabaena and Cylindrospermopsis in both the littoral and pelagic
waters. Relatively high diatom biomass was recorded in the pelagic compar
ed to the
littoral areas
,
but
Aulacoseira (Melosira), the formally dominant diatom species was
rarely encountered. Compared to previous records, the invertebrate community
composition has remained relatively stable despite drastic changes in water quality
and
fish stocks
, but changes in abundance were evident
.
Zooplankton densities were generally
higher in the littoral than pelagic zones. The abundance of Caridina nilotica, lake fly
larvae, and other invertebrates have increased in the lake with the decline
of
haplochromine stocks. Comparison of present zooplankton density estimates with previous
records indicates no marked differences in abundance patterns over the past 15 years
suggesting a stable and dependable resource to sustain water quality and fisher
y
-
related
functions. The OECD indicators of trophic status indicate that the pelagic waters range
from mesotrophic to eutrophic and the littoral zones are hypertrophic.
In
order to stem further deterioration of lake water quality, management of
phosphorus
loading into the lake should be given urgent priority.