Whether generalists or specialists, wildlife species use habitats based on their structural, compositional, and climatic characteristics. This use may vary with life stage, age, or physiological condition of the animal, as well as weather, season, food availability, need for cover or shelter, and other factors. Our research focuses on understanding the intrinsic and extrinsic factors that drive wildlife habitat use patterns and population dynamics, using amphibians as a focal vertebrate group.
Below are other science projects associated with this project.
Wildlife Ecology and Conservation Biology Team (FRESC)
Below are publications associated with this project.
Genomics-informed delineation of conservation units in a desert amphibian
Transition of vegetation states positively affects harvester ants in the Great Basin, United States
Persistence at distributional edges: Columbia spotted frog habitat in the arid Great Basin, USA
Managing habitat to slow or reverse population declines of the Columbia spotted frog in the Northern Great Basin
Terrestrial movement patterns of western pond turtles (Actinemys marmorata) in central California
Long-term observations of Boreal Toads at an ARMI apex site
Landscape genetics of high mountain frog metapopulations
Taxonomic and geographic variation in oviposition by tailed frogs (Ascaphus spp)
Population structure of Columbia spotted frogs (Rana luteiventris) is strongly affected by the landscape
Lack of significant changes in the herpetofauna of Theodore Roosevelt National Park, North Dakota, since the 1920s
- Overview
Whether generalists or specialists, wildlife species use habitats based on their structural, compositional, and climatic characteristics. This use may vary with life stage, age, or physiological condition of the animal, as well as weather, season, food availability, need for cover or shelter, and other factors. Our research focuses on understanding the intrinsic and extrinsic factors that drive wildlife habitat use patterns and population dynamics, using amphibians as a focal vertebrate group.
- Science
Below are other science projects associated with this project.
Wildlife Ecology and Conservation Biology Team (FRESC)
Wildlife respond to changes in their environment, some of which are dramatic and others subtle. To fully understand the factors that drive changes in populations and communities, we need better information on wildlife ecology in natural and human-altered landscapes. We conduct research and provide technical assistance to address applied questions about the ecology and conservation of wildlife... - Publications
Below are publications associated with this project.
Genomics-informed delineation of conservation units in a desert amphibian
Delineating conservation units (CUs, e.g., evolutionarily significant units, ESUs, and management units, MUs) is critical to the recovery of declining species because CUs inform both listing status and management actions. Genomic data have strengths and limitations in informing CU delineation and related management questions in natural systems. We illustrate the value of using genomic data in combAuthorsBrenna R. Forester, Melanie Murphy, Chad Mellison, Jeffrey Petersen, David Pilliod, Rachel Van Horne, Jim Harvey, W. Chris FunkTransition of vegetation states positively affects harvester ants in the Great Basin, United States
Invasions by non-native plants can alter ecosystems such that new ecological states are reached, but less is known about how these transitions influence animal populations. Sagebrush (Artemisia tridentata) ecosystems are experiencing state changes because of fire and invasion by exotic annual grasses. Our goal was to study the effects of these state changes on the Owyhee and western harvester antsAuthorsJoseph D. Holbrook, David S. Pilliod, Robert Arkle, Janet L. Rachlow, Kerri T. Vierling, Michelle M. WiestPersistence at distributional edges: Columbia spotted frog habitat in the arid Great Basin, USA
A common challenge in the conservation of broadly distributed, yet imperiled species is understanding which factors facilitate persistence at distributional edges, locations where populations are often vulnerable to extirpation due to changes in climate, land use, or distributions of other species. For Columbia spotted frogs (Rana luteiventris) in the Great Basin (USA), a genetically distinct popuAuthorsRobert S. Arkle, David S. PilliodManaging habitat to slow or reverse population declines of the Columbia spotted frog in the Northern Great Basin
Evaluating the effectiveness of habitat management actions is critical to adaptive management strategies for conservation of imperiled species. We quantified the response of a Great Basin population of the Columbia spotted frog (Rana luteiventris) to multiple habitat improvement actions aimed to reduce threats and reverse population declines. We used mark-recapture data for 1,394 adult frogs thatAuthorsDavid S. Pilliod, Richard D. SchererTerrestrial movement patterns of western pond turtles (Actinemys marmorata) in central California
We used radio telemetry to track the terrestrial movements and seasonal habitat use patterns of Western Pond Turtles (Actinemys marmorata) near two ponds in the Carrizo Plain Ecological Reserve, California, USA. We captured 93 turtles in September 2005 and, of these, we tagged three males and six females(weighing > 300 g) with external transmitters. Tagged turtles traveled from 255–1,096 m over thAuthorsDavid S. Pilliod, Justin L. Welty, Robert StaffordLong-term observations of Boreal Toads at an ARMI apex site
The U.S. Geological Survey’s Amphibian Research and Monitoring Initiative (ARMI) is a national project with goals to monitor the status and trends of amphibians, conduct research on causes of declines, and provide information and support to management agencies for conservation of amphibian populations. ARMI activities are organized around extensive inventories and place-based monitoring (such as cAuthorsPaul Stephen Corn, Erin L. Muths, David S. PilliodLandscape genetics of high mountain frog metapopulations
Explaining functional connectivity among occupied habitats is crucial for understanding metapopulation dynamics and species ecology. Landscape genetics has primarily focused on elucidating how ecological features between observations influence gene flow. Functional connectivity, however, may be the result of both these between‐site (landscape resistance) landscape characteristics and at‐site (patcAuthorsM.A. Murphy, R. Dezzani, D. S. Pilliod, A. StorferTaxonomic and geographic variation in oviposition by tailed frogs (Ascaphus spp)
Tailed frogs (Ascaphus spp.) oviposit in cryptic locations in streams of the Pacific Northwest and Rocky Mountains. This aspect of their life history has restricted our understanding of their reproductive ecology. The recent split of A. montanus in the Rocky Mountains from A. truei was based on molecular differentiation, and comparisons of their ecology are limited. Our objectives were to provideAuthorsNancy E. Karraker, David S. Pilliod, M. J. Adams, Evelyn L. Bull, Paul Stephen Corn, Lowell V. Diller, Marc P. Hayes, Blake R. Hossack, Garth R. Hodgson, Erin J. Hyde, Kirk Lohman, Bradford R. Norman, Lisa M. Ollivier, Christopher A. Pearl, Charles R. PetersonPopulation structure of Columbia spotted frogs (Rana luteiventris) is strongly affected by the landscape
Landscape features such as mountains, rivers, and ecological gradients may strongly affect patterns of dispersal and gene flow among populations and thereby shape population dynamics and evolutionary trajectories. The landscape may have a particularly strong effect on patterns of dispersal and gene flow in amphibians because amphibians are thought to have poor dispersal abilities. We examined geneAuthorsW.C. Funk, M.S. Blouin, P. S. Corn, B.A. Maxell, D. S. Pilliod, S. Amish, F.W. AllendorfLack of significant changes in the herpetofauna of Theodore Roosevelt National Park, North Dakota, since the 1920s
We surveyed 88 upland wetlands and 12 1-km river sections for amphibians in Theodore Roosevelt National Park, North Dakota, during 2001–2002 to gather baseline data for future monitoring efforts and to evaluate changes in the distribution of species. We compared our results to collections of herpetofauna made during 1920–1922, 1954 and 1978–1979. The boreal chorus frog (Pseudacris maculata) was thAuthorsB. R. Hossack, P. S. Corn, D. S. Pilliod