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
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.

 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).

Eighty mammals, 26 birds, 217 reptiles, and 39 amphibians were recorded as road-kills during the study.

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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