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Demographics and Movements of Chipmunks in a Fragmented Landscape
Lauren Rule1 and Tom Nelson2
1Wake Forest University, Winston-Salem, North
Carolina. 2Eastern Illinois University, Charleston, Illinois.
Introduction
Forest fragmentation occurs when large forests are cut, resulting in reduced
size and increased isolation of the remaining forest patches (Figure
1). Specifically, it
involves a reduction in total forest habitat, a reduction in patch size, an
increased edge-to-interior ratio and an increased distance between patches.
The effects of fragmentation on wildlife species may include a reduction in the
availability of suitable habitat, a decrease in quantity and diversity of food,
an increase in predation and parasitism and decreased genetic variability. These
factors lead to increased risk of local extinction within patches and decreased
probability of re-colonization following extinctions. Fragmentation
affects the ecology of species at the individual, population and community
levels (Nupp & Swihart 1998). Chipmunks do not inhabit agricultural fields, but
tree lines and fencerows can provide corridors for dispersal between forest
patches (Figure 2) (Henderson et al. 1985). Studies designed to measure faunal diversity
have shown that chipmunks are not present in small forest patches (Rosenblatt et
al. 1999). Nupp & Swihart (1998) suggested that chipmunks might have higher
predation rates in small forest patches.
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Figure 1.
Fragmented forest
patches in Central Illinois. |
Figure 2.
Fencerows may serve as corridors for dispersal |
Objectives
1. Describe the demographics of chipmunk
populations in relatively small and large forest patches.
2. Estimate home range sizes and maximum distances traveled.
3. Investigate which landscape features serve as barriers to movement.
Methods
This study was conducted during a ten-week period from June-August 1999. Two
forest patches (one large and one small) in central Illinois served as study
areas. Chipmunks were live-trapped using Sherman traps. Each animal was
classified by age and sex, weighed, measured, and marked with ear tags (Figure
4). Selected
individuals were radio-collared. Radio-tagged chipmunks were located daily
using a directional antenna and receiver to measure home range size and maximum
daily movements. Three individuals were subsequently moved to new
locations to investigate the effects of landscape barriers.
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Figure 4. Ear-tagged chipmunk |
Results
Demographics: We trapped thirty-five individual
chipmunks on two study sites and put radio-collars on six of these.
Estimated densities were similar on each study area (8.1/ha vs 7.3/ha for
small and large patches, respectively). Adults comprised 62% of the
population in the large patch but only 27% in the small patch. Sex ratios
did not differ between patches (Figures 4 and 5).
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Figure 5.
Chipmunk sex-age ratio in small forest patches |
Figure 6.
Chipmunk sex-age ratio in large forest patches |
Home Range & Movements: Summer home range size
averaged 1.1 ha for all six radio-collared chipmunks. Adult males tended
to have much larger home ranges (mean = 2.0 ha) than adult females and
juveniles (mean = 0.3 ha). However, mean home range size did not differ
between individuals in the large versus small forest patches. The
mean maximum linear distance traveled by radio-collared chipmunks was 188
meters. Adults males moved over longer linear distances than adult females
or juveniles. The maximum linear distance moved by any chipmunk was 390
meters.
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Figure 7.
Home ranges of five chipmunks in small forest
patch. |
Agricultural Fields as Barriers to Movement: Adult
male chipmunks moved 100, 200 and 300 meters away from the edges of their
home ranges returned home within hours of release if they could travel in
forest or along forested corridors. However, an individual moved ~200 m
across a cornfield that lacked any fencerow or forested corridor would not
cross the field and established a new home range near the release site.
Conclusions
These preliminary data suggest that chipmunks may be vulnerable to forest
fragmentation when woodlots are surrounded and isolated by row crops. Isolated
woodlots smaller than 1-2 ha may be too small to sustain viable chipmunk
populations.
Acknowledgements
This project was funded by the National Science Foundation and
Eastern Illinois University through the Research Experiences for Undergraduates
Program.
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