Wolverine Occupancy, Spatial Distribution, and Monitoring Design

  • Paul M. Lukacs
  • , Diane Evans Mack
  • , Robert Inman
  • , Justin A. Gude
  • , Jacob S. Ivan
  • , Robert P. Lanka
  • , Jeffrey C. Lewis
  • , Robert A. Long
  • , Rex Sallabanks
  • , Zack Walker
  • , Stacy Courville
  • , Scott Jackson
  • , Rick Kahn
  • , Michael K. Schwartz
  • , Stephen C. Torbit
  • , John S. Waller
  • , Kathleen Carroll

Research output: Contribution to journalArticlepeer-review

25 Scopus citations

Abstract

In the western United States, wolverines (Gulo gulo) typically occupy high-elevation habitats. Because wolverine populations occur in vast, remote areas across multiple states, biologists have an imperfect understanding of this species' current distribution and population status. The historical extirpation of the wolverine, a subsequent period of recovery, and the lack of a coordinated monitoring program in the western United States to determine their current distribution further complicate understanding of their population status. We sought to define the limits to the current distribution, identify potential gaps in distribution, and provide a baseline dataset for future monitoring and analysis of factors contributing to changes in distribution of wolverines across 4 western states. We used remotely triggered camera stations and hair snares to detect wolverines across randomly selected 15-km × 15-km cells in Idaho, Montana, Washington, and Wyoming, USA, during winters 2016 and 2017. We used spatial occupancy models to examine patterns in wolverine distribution. We also examined the influence of proportion of the cell containing predicted wolverine habitat, human-modified land, and green vegetation, and area of the cluster of contiguous sampling cells. We sampled 183 (28.9%) of 633 cells that comprised a suspected wolverine range in these 4 states and we detected wolverines in 59 (32.2%) of these 183 sampled cells. We estimated that 268 cells (42.3%; 95% CI = 182–347) of the 633 cells were used by wolverines. Proportion of the cell containing modeled wolverine habitat was weakly positively correlated with wolverine occupancy, but no other covariates examined were correlated with wolverine occupancy. Occupancy rates (ψ) were highest in the Northern Continental Divide Ecosystem (ψ range = 0.8–1), intermediate in the Cascades and Central Mountains of Idaho (ψ range = 0.4–0.6), and lower in the Greater Yellowstone Ecosystem (ψ range = 0.1–0.3). We provide baseline data for future surveys of wolverine along with a design and protocol to conduct those surveys.

Original languageEnglish
Pages (from-to)841-851
Number of pages11
JournalJournal of Wildlife Management
Volume84
Issue number5
DOIs
StatePublished - Jul 1 2020

Funding

We thank the field technicians and volunteers who helped collect the data including B. Adkins, A. Arnold, A. Blackwood, B. Blount, S. Bodle, B. Bosworth, M. Feiger, C. Klingler, C. McCullough, L. Ferguson, K. Nelson, P. Ott, I. Smith, K. Voll, J. Wagner, B. Wagner, A. Welander, J. Lex, W. Cole, V. Villalobos, D. Madel, M. Davidson, S. Clairmont, R. Adams, A. Moran, K. Wyant, P. Adams, P. Alexander, M. Ruby, R. Yates, L. Strong, A. Jacobs, A. Anderson, C. Waters, J. Swanson, L. Breidinger, R. Vinkey, E. Graham, S. Tomson, L. Lamar, A. Lieberg, M. Mayernik, P. Shanley, L. Bate, G. Byrd, L. Byrd, K. Chickering, J. George, J. Griswold, K. Kendall, K. Lynch, T. Malish, C. Menzel, P. Metzmaker, D. Moore, B. Polley, J. Rossman, D. Savage, G. Sherman, D. Voerman, I. Wheeler, A. Zavadil, J. Akins, P. Debryn, R. Christopherson, S. Fitkin, D. Gaylord, C. Gaylord, J. Heinlen, M. Marsh, P. MacKay, S. Paz, J. Plumage, P. Reed, J. Rohrer, D. Volsen, A. Woodrow, F. Yarborough, D. Youkey, C. Atkinson, S. Halman, R. Kindermann, S. Ryder, and L. Tafelmeyer. N. Bjornlie implemented the project in Wyoming. Logistical support was provide by the Beaverhead‐Deerlodge, Bitterroot, Custer‐Gallatin, Flathead, Kootenai, Lewis and Clark‐Helena, Lolo, Mt. Baker‐Snoqualmie, Okanogan‐Wenatchee, Sawtooth, Boise, Payette, Salmon‐Challis, Nez Perce‐Clearwater, Panhandle, Caribou‐Targhee, Okanogan, Bridger‐Teton, Shoshoni and Bighorn National Forests; the Eastern Shoshoni and Northern Arapaho Tribes; Glacier, North Cascades, Grand Teton, and Yellowstone National Parks. We also thank the many individuals and organizations that volunteered to run supplemental stations including L. Lamar and Swan Valley Connections, E. Graham and Blackfoot Challenge, T. Walrath and Montana Trappers Association, P. Hough and Friends of Scotsman Peak, K. Paul and Wolverine Watchers, S. Gehman and Wild Things Unlimited, Idaho Conservation League volunteers, S. Bustinger, D. Heffington, C. Fager, V. Boccadori, D. Boyd, J. Kolbe, T. Smucker, T. Their, C. Hericks, D. Scharf, J. Brooks, C. Gower, A. Nelson, J. Brooks, R. LeBlanc, B. Cunningham. This work was funded by the USFWS through a Competitive State Wildlife Grant, Great Northern Landscape Conservation Cooperative grant, and Mountain–Prairie Regional Science Grant; the National Fish and Wildlife Foundation; the United States Forest Service Carnivore Program; and the state fish and wildlife agencies that spearheaded the work. We thank the Western Association of Fish and Wildlife Agencies for administering grants.

    Keywords

    • Idaho
    • Montana
    • Washington
    • Wyoming
    • camera trap
    • occupancy
    • sampling rare species
    • wolverine

    Fingerprint

    Dive into the research topics of 'Wolverine Occupancy, Spatial Distribution, and Monitoring Design'. Together they form a unique fingerprint.

    Cite this