dc.description.abstract |
Water quality monito
ring activities were carried out on physical
-
chemical
parameters, water chemistry and biotic indices at selected littoral and pelagic stations
along north
-
south and east
-
west transects over an annual cycle between 2000 and 2005.
The activities were aimed a
t collecting baseline information and data for use to define the
current lake conditions and make a water quality assessment of the lake in relation to
nutrient/ pollutant loadings as a basis for future monitoring surveys. As much as possible
current condi
tions of the lake were compared to pa
st observations where field
sites
coincided with those of historical studies.
Littoral stations (0
-
20m) showed higher temperatures, pH, turbidities and
electrical conductivity while Secchi depths and dissolved oxygen w
ere lower compared to
pelagic ones. Deeper
pelagic sites experience thermal
stratification, leading to strong
differences between surface and deep water layers especially in terms of temperature and
dissolved oxygen except for
June through August during wh
ich
the lake
achieves
complete mixing in all stations
. On average, littoral stations have higher total nitrogen,
chlorophyll, organic matter as well as total particulate carbon. Phytoplankton
production and biomass in shallow inshore sites is light
-
limited
due to self shading and
the latter can therefore sustain
higher
algal biomasses
because of limited mixing depths
.
Nitrogen often
limits algal growth except for C
yanobacteria that can fix atmospheric
nitrogen to meet their N limitations. The higher algal b
iomass accounts for the higher TN
concentrations, chlorophyll and organic matter at littoral sites. During thermal
stratification, TP and SRP concentrations are comparable in littoral and pelagic sites
while during and just after mixing, both fractions of
P are higher in the littoral areas. Regional
Lake Victoria Environment Report
Water Quality and Ecosystems
Component
Lake Victoria Environment
al
Management Project
63
Continuous
excess SRP and the ability of C
yanobacteria to fix atmospheric nitrogen
create nutrient saturated conditions that result in light limitation for algal growth.
Annual rainfall is characterised by two peaks in t
he
stratification seasons
2 and 3 and
appears to be the main source of nutrient enrichment in the lake, particularly TP.
Decomposition of organic matter during the stratification period results into release of
TP and Si
into deeper waters
where they build
up to much greater concentration than in
surface waters. TN reaches annual minimum during
the deep
mixing
period because of
N
-
poor deep waters. Chlorophyll concentrations also reach their annual minimum at this
time as deep mixing imposes strong light limi
tation on algal growth and nitrogen fixation
especially in pelagic areas
.
Comparisons with historical records show that the lake today is warmer than in
the 1960s but with lower oxygen and pH in the deeper waters. Thus deep water
respiration
rates, oxygen
consumption and CO
2
are higher in the 2000s largely attributed
to the eu
trophication of the lake.
Oxygen depletion
in deeper waters d
uring thermal
stratification has
led to loss of habitat for fish and other biota. Chlorophyll levels,
phosphorus concentra
tions and electrical conductivity in both littoral and pelagic
stations have increased compared to records of the 1960s. On the other hand nitrogen
concentrations around marginal bays and gulfs have not shown a marked increase
compared to historical record
s of the 1960s and 1970s. Dissolved
silicon
in the pelagic
areas has decreased 5
-
20 times compared to historical records as eutrophication has
increased Si demand by diatoms relative to rather constant supply from the catchment. In
line with increased
alga
l
turbidities, Secchi depths have decreased
at least
two
-
fold since
the 1960s. The need for lake wide regular water quality surveys and basin developments
in support of appropriate management interventions can not be overemphasized at
present
in order to d
etermine whether the lake is continuing along the same trends over
time documented in this report. |
en_US |