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Scientific
Method and Hypothesis Testing
an exercise in applying the scientific method
Observations
The macroinvertebrate community structure in a stream can vary due to
a number of physical, chemical, and biological factors. These factors
can come from both terrestrial and aquatic sources. Changes in the terrestrial
landscape may have direct or indirect effects on the number and types
of macroinvertebrates present in a stream. In the eastern United States,
hemlock forests are dying due to an exotic pest, the hemlock wooly adelgid
(HWA). Because hemlocks can be an important component of the riparian
terrestrial structure, the loss of these trees represents a potential
changing factor for the stream ecosystem.
Hypothesis
In streams of similar size, type and gradient, streams in hemlock forests
of different level of infestation with hemlock wooly adelgid will show
different macroinvertebrate community structure.
Experiments
Nine stream sites in three different levels of HWA infestation in hemlock-dominanted
forests were identified. The three levels of infestation were non-infested
forest (healthy hemlock), 50% infestation, and 100% infestation (all hemlocks
in area affected). Three sites were located in each infestation type.
All sites were similar in watershed size, stream order, gradient, benthic
substrate, and forest composition.
Stream macroinvertebrate samples were collected at all sites following
the EPA's Rapid Bioassessment Protocol. The collected organisms were identified
and placed into one of four functional feeding groups: scraper, shredder,
predator, or collector. Relative percentage of total organisms in each
functional feeding group was determined for each level of HWA infestation
by averaging the percentages for each site within the level.
Data
Data disproving the hypothesis - shows no change in functional
feeding groups
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% shredders
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% predators
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% scrapers
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% collectors
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0% affected
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18
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20
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30
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32
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50% affected
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21
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18
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27
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34
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100% affected
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20
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19
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29
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32
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Data supporting the hypothesis - shows a change in the functional
feeding groups
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% shredders
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% predators
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% scrapers
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% collectors
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0% affected
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18
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20
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30
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32
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50% affected
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20
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20
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35
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25
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100% affected
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26
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15
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39
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20
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Conclusion
Though there was some variability, functional feeding group analysis shows
that there is a general trend toward a change in the macroinvertebrate
community as hemlock wooly adelgid affects the health of the hemlock trees
around streams. The most affected functional feeding groups appear to
be the scrapers and the shredders, two groups that rely on outside inputs.
Scrapers mainly feed on attached algae; algal growth would increase with
increasing amounts of sunlight reaching the stream as the riparian tree
cover is lost. Shredders rely mainly on organic input from the terrestrial
environment; as hemlock trees are affected by the HWA infestation, the
trees drop their needles, increasing organic input to the stream.
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