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Natural Areas Association
P.O. Box 1504, Bend, OR 97709
Telephone: (541) 317-0199
Fax: (541) 317-0140
Email: mail@naturalarea.org
Web: www.naturalarea.org
Mission
The mission of the Natural Areas Association
is to advance the preservation of natural
diversity. The Association works to inform,
unite, and support persons engaged in
identifying, protecting, managing and
studying natural areas and biological
diversity across landscapes and ecosystems.
Board Officers
Kim Herman, President
Michigan Department of Natural Resources
Lisa Smith, Vice President
Consultant - Stahlstown, Pennsylvania
Karen Smith, Secretary
Arkansas Natural Heritage Commission
Randy R. Heidorn, Treasurer
Illinois Nature Preserves Commission
Board of Directors
David Borneman
Ann Arbor Department of Parks & Recreation
Brian Bowen
Tennessee Natural Areas Program
Ruark Cleary
Florida Department of Environmental Protection
Ronald Hiebert
National Park Service, Flagstaff, Arizona
Renee Kivikko
Land Trust Alliance
Vickie L. Larson
Consultant, Merritt Island, Florida
Thomas Meyer
Wisconsin Department of Natural Resources
Timothy Nigh
Missouri Department of Conservation
Charles Nilon, Jr.
University of Missouri, Columbia
Randy Nyboer
Illinois Natural History Survey
Pene Speaks
Washington Department of Natural Resources
Jil Swearingen
National Park Service, Washington, D. C.
Appointments & Liaisons
Steven Link, Natural Areas Journal Editor
Washington State University - Tri-Cities
Steve Shelly (Liaison)
USDA Forest Service, Missoula, Montana
Natural Area News
Co-Editors: Ruark Cleary/Deb Kraus
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Wildlife Road-kills in a Southeast Florida Park
A Steward’s Circle Note
Robin J. Rossmanith, and Henry T. Smith Road-kills of wildlife are an international
conservation dilemma (Skoog 1982;
Smith et al. 1994; Trombulak and Frissell
2000; Hels and Buchwald 2001; Bard et al.
2002; Fahrig et al. 2002; Smith et al. 2003).
Wildlife killed by vehicles has prompted
investigators to research ways to mitigate
kills including reduced speed limits, physical
barriers, and environmental education (Foster
and Humphrey 1995; Bertwistle 1999; Brown
et al. 1999; Evink 1999; Phillips 1999; Bard et
al. 2002; Foresman 2002).
This note reports
wildlife mortality
due to collisions with
vehicles during 1995
to 1998 at Jonathan
Dickinson State Park
(JDSP), a 4644.1 ha, mixed-use state park
located approximately 40 km north of West
Palm Beach, on Florida’s southeast coast.
JDSP is a mix of uplands and wetlands,
consisting mostly of four ecosystems: wet
pine flatwoods (1983.8 ha), scrub (935.2 ha),
strand swamp (370.9 ha), and wet prairie
(351.8 ha; Florida Park Service, 2000).
Methods: An opportunistic, daily road-kill
survey was conducted during 1995-1998
by JDSP park staff and consisted of slowly
searching road surfaces (ca. 8-24 km/hr.) for
dead wildlife (i.e. Smith et al. 1994; Bard et
al. 2002).
At JDSP, ca. ten km of paved, two-lane road
(with widely variable speed limits of 24.2-
48.4 km/hr) were first driven daily between
0745 and 0815 and provided opportunistic
collection of vertebrate wildlife taxa struck by
moving vehicles. Animals were identified to
species when possible.
Results: Eighty mammals, 26 birds, 217
reptiles, and 39 amphibians were recorded as
road-kills during the study (Table 1). There
was a significant difference in road-kill
frequency goodness of fit between the four
pooled classes of animals (x2 = 253.31, df =
3, P < 0.05, Table 1). Armadillos (Dasypus
novemcinctus) had the highest frequency
(23) among mammals and black racers
(Coluber constrictor; 42) and garter/ribbon
snakes (Thamnophis spp.; 41) were the
most frequent reptiles killed. Birds and amphibians exhibited no clear trends in vulnerability.
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Discussion: While managing for natural
resources and resource-based human recreation
it is inevitable that humans will impact the
natural resources. Ten species of mammals,
most commonly the exotic nine-banded
armadillo (23), were found (Layne 1997). We
conjecture that armadillos have achieved a
relatively high population-density at JDSP,
and combined with a predilection for foraging
along disturbed roadside areas, are extremely
vulnerable to road-kill events. We were
surprised that another common exotic mammal,
feral hog (Sus scrofa) was never found to be
killed by a vehicle (Engeman et al. 2003). We
attribute this phenomenon to the wariness of the
species (Saunders and Bryant 1988).
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Eighty mammals, 26 birds, 217 reptiles, and 39 amphibians
were recorded as road-kills during the study.
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Thirteen species of birds totaling 26
individuals were killed by collisions with
vehicles. By comparison, (Fahrig et al. 2002)
in a five-year study conducted in Key Largo,
Florida, reported higher numbers of bird
kills including various warblers, chuck-will’swidows
(Caprimulgus carolinensis), and gray
catbirds (Dumetella carolinensis). A number
of synergistic factors contributed these
differences in findings of avian mortality
species: including differences in latitude,
vegetation community cover types, and road
use and speed limits. The situation with
birds also is atypical in that some species can
nest successfully very close to roadsides even
with high levels of traffic (Smith et al. 1993;
Rodgers and Smith 1995; Loftin and Smith
1996). Our data suggest the majority of the
bird fauna within JDSP are relatively secure
from threat of road-kill.
Sixty percent of the animals killed by vehicles
were reptiles (52% snakes) and 11% were
amphibians. The high number of reptiles
killed on roads can probably be attributed to
their ectothermic nature (Pough et al. 2001).
Conversely, the low number of amphibians
found could be partially explained by
three theories: (1) typically amphibians are
smaller in body size than the other classes
of vertebrates and therefore less likely to be
struck by vehicles; (2) and many amphibians
found in JDSP are nocturnally active, when
humans are less likely to drive; and (3) the
small sizes of amphibian road-kills may
contribute to them being overlooked during
surveys.
Protective closures and buffer zones have been
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