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Proceedings of the Ninth Mountain Lion Workshop - Carnivore ...

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Using DNA to Estimate Cougar Populations: a Collaborative Approach<br />

Richard A. Beausoleil, Washington Department <strong>of</strong> Fish and Wildlife, 3515 State<br />

Highway 97A, Wenatchee, WA 98801, USA, beausrab@dfw.wa.gov<br />

Kenneth A. Warheit, Washington Department <strong>of</strong> Fish and Wildlife, 600 Capitol Way<br />

North, Olympia, WA 98501-1091, USA, warhekiw@dfw.wa.gov<br />

Wan-Ying Chang, Washington Department <strong>of</strong> Fish and Wildlife, 600 Capitol Way North,<br />

Olympia, WA 98501-1091, USA, changwyc@dfw.wa.gov<br />

Donald A. Martorello, Washington Department <strong>of</strong> Fish and Wildlife, 600 Capitol Way<br />

North, Olympia, WA 98501-1091, USA, martodam@dfw.wa.gov<br />

John D. Pierce, Washington Department <strong>of</strong> Fish and Wildlife, 600 Capitol Way North,<br />

Olympia, WA 98501-1091, USA, piercdjp@dfw.wa.gov<br />

ABSTRACT To better understand population dynamics <strong>of</strong> cougar, agency managers need<br />

long-term data sets collected using standardized methodologies. Short-term studies,<br />

while useful for management, are only “snapshots in time”, and provide little information<br />

about year-to-year variability or long-term status. None<strong>the</strong>less, wildlife agencies are<br />

typically only able to conduct population estimation projects for 5 years or less because<br />

<strong>of</strong> expenses associated with current research methodologies. The objectives <strong>of</strong> this<br />

project were to: (1) acquire a scientific population estimate <strong>of</strong> cougars in nor<strong>the</strong>ast<br />

Washington; (2) test <strong>the</strong> efficacy and practicality <strong>of</strong> using DNA capture techniques to<br />

estimate cougar population size; (3) manage project costs to allow agencies interested in<br />

<strong>the</strong> technique to potentially conduct <strong>the</strong> research for decades. We used a capturerecovery<br />

methodology but instead <strong>of</strong> using conventional markers (i.e., radio collars,<br />

eartags and tattoos), we used DNA from tissue samples collected from treed cougar as<br />

our “capture” and DNA samples collected from harvested cougar as our “recovery”. We<br />

tested 5 biopsy dart types from 3 different manufacturers to collect <strong>the</strong> samples from<br />

treed cougars. For <strong>the</strong> “capture” sample, volunteer hound handlers were deployed<br />

throughout <strong>the</strong> project area between 01 November and 31 December (2003-current) to<br />

tree cougars using hounds and obtain a DNA sample via a biopsy dart and CO2 powered<br />

rifle. There was no physical handling required and once a sample was retrieved, <strong>the</strong><br />

cougar was immediately left in <strong>the</strong> tree. Each hound handler was assigned to a specific<br />

portion <strong>of</strong> <strong>the</strong> project area and each was required to work 20-25 days within <strong>the</strong> allotted<br />

timeframe. The “recovery” phase immediately followed <strong>the</strong> “mark” period (01 January<br />

to 31 March) each year. During <strong>the</strong> hunting season agency personnel collected a tissue<br />

sample from all cougar mortalities statewide via a mandatory reporting system. DNA<br />

from both samples was analyzed using micro-satellite analysis. The DNA fingerprint<br />

analysis consisted <strong>of</strong> positively identifying 28-36 alleles (14-18 loci) for each tissue<br />

sample. Samples that did not produce a minimum <strong>of</strong> 14 loci were censored. We<br />

extracted <strong>the</strong> specified number <strong>of</strong> loci from 128 <strong>of</strong> 163 cougar samples resulting in<br />

identification <strong>of</strong> 100 individual cougars in <strong>the</strong> “capture” sessions. In <strong>the</strong> “recovery”<br />

sessions, over 62 tissue samples were collected and analyzed from within <strong>the</strong> project<br />

area. Sixteen <strong>of</strong> <strong>the</strong> 62 recoveries were previously “captured”. We used Program MARK<br />

to estimate population size, which resulted in an average within-year population estimate<br />

<strong>of</strong> 43 cougars (CI 34-58) or 0.87 (CI = 0.65-1.1) cougars per 100km 2 . Over <strong>the</strong> 4 years, it<br />

appears that <strong>the</strong> cougar population has declined. The cost <strong>of</strong> <strong>the</strong> DNA project in year 1<br />

was $24,110. However because that included microsatellite plates (a one-time expense)<br />

<strong>Proceedings</strong> <strong>of</strong> <strong>the</strong> <strong>Ninth</strong> <strong>Mountain</strong> <strong>Lion</strong> <strong>Workshop</strong><br />

160

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