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Effects
of Riparian Zone Fragmentation on Primary Productivity
and Fish Growth Rates
Krista
Kirkham and Robert Fischer
Department
of Biological Sciences, Eastern Illinois University
Introduction
Stream
habitat fragmentation.
What is stream habitat fragmentation?
A lack of connectivity between upstream and downstream
populations.
What causes fragmentation?
Human interference--agriculture, pollution, industry, forestry, erosion.
Outcome of Fragmentation
Less than 1% of original landscape remains in Illinois
Distinct patch formation may occur within a stream.
Effects of
fragmentation.
Abiotic effects include increased amounts of sedimentation, siltation,
chemical runoff, and pollution as well as changes in dissolved oxygen, temperature, and pH.
Biotic
effects include negative effects upon diversity, richness, mortality and
reproductive success as well as a disruption of habitat equilibrium.
Since stream
habitat fragmentation can cause changes to an abiotic environment of a stream,
one would also expect to see changes in primary productivity which may lead to
changes in growth rates of fish at various trophic levels.
Objectives
1. Determine
if habitat fragmentation exists in stream environments.
2. Discover
if primary productivity is different between patches.
3. Determine
if growth rates of fish are affected by differences in primary productivity
between patches.
4. Observe
the consistency of energy distribution between trophic levels
in comparison to varied growth rates.
Methods
Seven
sites were sampled for fish and productivity along Polecat Creek,
a 4th order tributary of the Embarras River. Reaches
were 300 ft and contained at least one riffle/pool sequence
when possible.
Sampling
techniques included electroshocking, collection,
identification, and measurement of fish, then selection of fish
for growth determination.
Results
Habitat
assessment used
Stream Habitat Assessment Procedure (SHAP). SHAP
Assessment is based on fifteen habitat metrics associated within
the following three broad categories:
1. Substrate
and instream cover.
2, Channel
hydrology and morphology.
3, Riparian and
bank features.
|
 |
 |
 |
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Good
quality habitat |
Poor quality habitat. |
SHAP score, significant difference between sites (p<0.0001) |
Productivity
assessment used a biostimulation
technique, testing
for the growth of Selenastrum capricornutum in the presence of
turbidity.
 |
Growth rates of S. capricornutum with phosphorus (P) and nitrogen (N)
treatments. |
Growth rate was determined
by using the back calculation technique.
|
 |
Bluntnose minnow (Pimephales notatus) length vs.
age at good and poor sites. |
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|
|
 |
Longear sunfish (Lepomis megalotis) length vs. age at
good and poor sites. |
Conclusions
1. Distinct
patches can be formed in stream habitats in response to land use.
2. All
sites in Polecat Creek showed limited productivity due to nutrient
deficiency.
3. Additional
productivity analysis showed phosphorus to be the limiting nutrient.
4. Growth
rates of fish at different trophic levels in each patch were not affected by
productivity differences. |