Source: UNIVERSITY OF WASHINGTON submitted to
ECOLOGY AND CONSERVATION OF THE WESTERN GRAY SQUIRREL (SCIURUS GRISEUS) IN THE NORTH CASCADES
Sponsoring Institution
Other Cooperating Institutions
Project Status
TERMINATED
Funding Source
Reporting Frequency
Annual
Accession No.
0226239
Grant No.
(N/A)
Project No.
WNZ-A65785
Proposal No.
(N/A)
Multistate No.
(N/A)
Program Code
(N/A)
Project Start Date
Apr 1, 2011
Project End Date
Jun 30, 2012
Grant Year
(N/A)
Project Director
West, S.
Recipient Organization
UNIVERSITY OF WASHINGTON
4333 BROOKLYN AVE NE
SEATTLE,WA 98195
Performing Department
Wildlife Science
Non Technical Summary
The western gray squirrel (Sciurus griseus) is the largest native tree squirrel to Washington, and was listed as threatened in 1993 by the Washington Department of Fish and Wildlife (WDFW). Once ranging more widely in eastern and western Washington state, western gray squirrels are currently confined to three geographically isolated areas: in Pierce County in the southern Puget Trough, in southern Washington in Klickitat, Yakima, and Skamania counties, and in north central Washington in Chelan and Okanogan counties. Recovery of the species has become a priority, however, distributional and life history data on the western gray squirrel, particularly for the North Cascades population, is limited. Objectives: 1. Where are western gray squirrels distributed in the North Cascades 2. What types of habitats do western gray squirrels select in the North Cascades 3. What behavioral adaptations allow western gray squirrels to live in the North Cascades 4. How do we best conserve western gray squirrels in the North Cascades Results of this project will inform western gray squirrel conservation and habitat management.
Animal Health Component
(N/A)
Research Effort Categories
Basic
(N/A)
Applied
100%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1350860107060%
1350860108020%
1350860303020%
Goals / Objectives
Specific Objectives: 1. Characterize current western gray squirrel distribution relative to areas treated to reduce forest fire fuels (treatment areas) and areas recently burned by wildfire. 2. Identify and compare western gray squirrel nest sites and high and low habitat use areas relative to fire fuel reduction treatments and areas experiencing recent wildfire. 3. Measure genetic relatedness of western gray squirrels with respect to spatial location, home range overlap, and co-nesting occurrence. 4. Compare genetic diversity of western gray squirrels in the North Cascades to squirrels in the Puget Trough and Klickitat populations and estimate effective population size of the North Cascade population. 5. Examine changes in activity patterns of western gray squirrels between winter and summer. 6. Document and compare seasonal diet of western gray squirrels in the North Cascades. 7. Evaluate change in knowledge and attitude towards western gray squirrel research after communicating scientific process and findings to the general public using alternate communication strategies. Results will be provided directly to land managers including those in the USGS, NPS, U.S. Forest Service, and WDFW to be incorporated into land management and conservation plans for the western gray squirrel and its habitat. Timeline: Squirrel trapping/telemetry: April-September 2011. Communication treatments and surveys: April-June 2011. Presentation: American Society of Mammalogists 91st Annual Meeting: June 24-June 29th 2011. Habitat sampling with hourly assistants: July-September 2011. Data analysis and writing of dissertation and peer reviewed journal articles: Fall Quarter 2011, Winter Quarter 2012. 6th International Colloquium on Arboreal Squirrels Kyoto, Japan: February 4-8 2012. Dissertation defense: March 2012. Presentation at the Washington Chapter of the Wildlife Society Meeting: March 2012. Presentation of results to local communities: Stehekin and the Methow Valley: April 2012. Journal articles published: Late 2012, early 2013.
Project Methods
We will document western gray squirrel distribution and occupancy in the North Cascades and guide live trapping efforts using hair snag tubes in two study areas. Squirrels will be live-trapped and radio-collars will be attached. Captured squirrels will be marked with ear-tags, weighed, sexed, and examined for body and reproductive condition. An ear punch will be used for DNA analysis. Fecal samples will also be collected when possible. Radio-collared squirrels will be relocated with homing. Squirrels will be tracked and locations confirmed with visual sightings. The condition of the animal and behavior will also be documented when possible. Coordinates will be recorded and plotted on Geographic Information Systems (GIS) maps. Habitat characteristics will be measured for each location. We will examine tree locations for nests, and if found record the coordinates, tree and nest characteristics, and what squirrels have been located there. Co-nesting by radio-collared squirrels will be recorded. Nests will be marked and photographs will be taken when possible. The collection of locations for each squirrel will be plotted in a GIS and home range sizes will be calculated. Utilization distributions (UDs) will be compared to habitat variables: existing GIS layers and ground measurements of variables. The same habitat variables will also be measured at nest sites to examine resource selection at multiple scales. An average Resource Utilization Function (RUF) for all squirrels will also be calculated and used to predict resource utilization in areas not sampled (based on GIS habitat layers) allowing identification of potential habitat patches outside the immediate study area. We currently have information on 16 squirrels at each study site. We need sufficient radio locations from another 10-15 squirrels to adequately test for differences between squirrel use of control and fire fuel treated sites, a key question of this research. Given squirrel capture rates in the area over the past summer we expect to accomplish this with one more field season. For genetic analysis, Washington Department of Fish and Wildlife will screen microsatellites at 18 loci previously isolated for western gray squirrels. Prior to any microsatellite analysis we will check for genotyping errors. We will conduct analyses on four populations: Stehekin, the entire North Cascades, Fort Lewis, and Klickitat County. We will examine western gray squirrel relatedness, estimate the proportion of parents sampled, compare relatedness and parentage, and evaluate effective population size. For diet analysis squirrel fecal pellets will be dissected and examined. Fungal spores will be identified to genus when possible with relative abundance estimated per sample. Results will be compared between seasons, squirrels, and study sites. We will determine which diet items (fungal spores) drive differences between samples. We will also assess the effectiveness of science communication to the general public.

Progress 04/01/11 to 06/30/12

Outputs
OUTPUTS: This project funded by the Skagit Valley Wildlife Research Grant Program of Seattle City Light provided funding for a final field season on the project, Western Gray Squirrel: Measure Distribution, Abundance, and Habitat Use in Lake Chelan National Recreation Area, Washington (WNZ-1285). The final report for the primary project is given below: Fieldwork on this project has concluded. A successful dissertation defense was accomplished in May 2012. Reports of work "in progress" for this project were given at several scientific meetings in previous years and for residents of Stehekin and the Methow Valley, Washington. Results of this study were also given at seminars and public presentations at the University of Washington. Papers for publication in scientific journals are in preparation. PARTICIPANTS: Collaborators at the University of Washington included: Dr. Gordon Bradley: UW faculty colleague and graduate committee member. Dr. Lorentz Hauser: UW faculty colleague and graduate committee member. Dr. Joseph Ammirati, project advisor. Dr. Loveday Conquest, statistical consulting. Kathryn D. Stuart, Ph.C. / Ph.D.: graduate student supported by the project. Collaborating individuals outside the University of Washington included: Dr. Mathew Vander Haegen, Washington Department of Fish & Wildlife: graduate committee member. Dr. Kurt Jenkins, USGS, graduate committee member. Robert Kuntz, National Park Service, project advisor. Vicki Gempko, National Park Service, logistical support and radiotelemetry. Dr. James Trappe, Oregon State University, project advisor. Cherrill Bowman, Washington Department of Fish and Wildlife, genetic tissue analysis. Kristin Mansfield and Charles Leathers, Washington Animal Disease Diagnostic Laboratory, Washington State University, necropsies and histology. Dave Volson, U.S. Forest Service, logistical support. John Rohrer. U.S. Forest Service, logistical support. Peter Morrison, Pacific Biodiversity Institute, GIS support. Collaborating organizations included: Washington Department of Fish & Wildlife. School of Environmental and Forest Sciences, University of Washington. School of Aquatic and Fishery Sciences, University of Washington. Department of Biology, University of Washington. Pacific Northwest Cooperative Ecosystem Studies Unit. National Park Service. U.S. Geological Survey. U.S. Forest Service, Wenatchee and Winthrop stations. The Wildlife Society, Washington Chapter. The Methow Conservancy. Pacific Biodiversity Institute. Seattle City Light. Washington Animal Disease Diagnostic Laboratory, Washington State University. TARGET AUDIENCES: Because this study dealt with a state-threatened species on National Park, National Forest, and private lands, its response to ongoing fire fuel reduction plans are of widespread interest. Studied populations were located at the northern periphery of the species range, and before this project were the focus of only one study, one that did not address fire fuel reduction impacts, winter ecology, diet, genetics, or alternative means of information transfer to the public. How these populations compared to others in the state and the northwest were of interest not only to wildlife conservationists and land managers, but the public as well. PROJECT MODIFICATIONS: In the spring of 2011 we expanded the initial study area around Stehekin eastward into the Methow Valley. This was done with financial assistance from the Skagit Valley Wildlife Research Grant Program of Seattle City Light. We expanded the study area to arrive at statistically adequate sample sizes and to extend the project's scope of inference more broadly to the northern population of the squirrel. Study approaches and methodologies were consistent throughout the study.

Impacts
The western gray squirrel (Sciurus griseus) was classified as a Washington State threatened species by the Washington Department of Fish and Wildlife in 1993 due to a decline in range and number. The North Cascades population is geographically and genetically isolated from others in Washington, Oregon, and California, and may be ecologically unique as it exists in a mixed-conifer forest habitat that lacks oak (Quercus spp.): a source of forage and maternal nests in most other portions of the range. The North Cascades are also distinguished by high average annual snowfall and cold temperatures, frequent wildfire and dynamic forest management. Land management agencies have initiated fire fuel reduction plans that may have potentially adverse effects on western gray squirrels. Local populations in Stehekin and the Methow Valley are likely small, making them susceptible to stochastic threats including genetic drift and inbreeding, which reduce evolutionary fitness and increase extinction risk. We studied distribution, life history, and response of squirrels to fire fuel treatments in the North Cascades from 2008-2011 using live trapping, radiotelemetry, and genetic and fecal sampling. Scientific communication between researchers and the general public was evaluated with interviews and an experimental study on the effectiveness of alternate communication methods. Squirrels used fire fuel treated areas disproportionately within their home ranges indicating that recent treatments and wildfires have not negatively affected western gray squirrel habitat at the home range scale. We also found no evidence that treatments and wildfire have negatively affected western gray squirrel diet. Areas used for nesting were characterized by large, tall trees, high levels of dwarf mistletoe infection, high canopy cover and connectivity; all characteristics that can decrease with fire fuel reduction treatments. Future treatments can focus on retaining patches of large trees with some mistletoe infection, and moderate levels of canopy cover and connectivity to conserve western gray squirrel nesting habitat in the North Cascades. Average home range size, degree of overlap, and effective population size indicate that the North Cascades may support a larger population of western gray squirrels than previously thought. Understanding and support for wildlife research increased significantly through science communication.

Publications

  • Stuart, K.D. 2012. Ecology and conservation of the western gray squirrel in the North Cascades. Ph.D. Dissertation, University of Washington, Seattle. 239p.