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

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Wilderness DAUs were considered valuable because <strong>the</strong>y served as reservoir areas<br />

where, due to difficult access and topography, lenient hunting seasons could be allowed<br />

without significantly reducing dispersal into adjacent areas like <strong>the</strong> Salmon DAU and<br />

parts <strong>of</strong> Warren DAU (Power 1985, Harris 1991). To evaluate changes in cougar harvest<br />

rate through time, we selected Unit 26 which is contained within <strong>the</strong> Frank Church River<br />

<strong>of</strong> No Return Wilderness area. In addition to state harvest records, four cougar research<br />

projects (Hornocker 1970, Seidensticker et al. 1973, Quigley et al. 1989, Akenson et al.<br />

2005) were conducted in Unit 26 resulting in cougar population estimates between 1969<br />

and 2003.<br />

DAU Comparisons<br />

We compared Idaho Department <strong>of</strong> Fish and Game cougar harvest data from <strong>the</strong> 1972-<br />

2006 Big Game Management Records database (B. Ackerman, Idaho Department <strong>of</strong> Fish<br />

and Game, unpublished data) from 2 areas (Warren DAU and Selway DAU) designated<br />

by Idaho Department <strong>of</strong> Fish and Game as source populations, an adjacent sink area<br />

(Salmon DAU), and 2 distant areas (Pocatello DAU and Oakley DAU) that historically<br />

had low harvest levels, but had increased harvest since <strong>the</strong> 1990s. We compared longterm<br />

harvest trends among DAUs from 1983-2006 and compared <strong>the</strong> mean proportion <strong>of</strong><br />

females in <strong>the</strong> harvest per decade (1980s, 1990s, 2000s) among DAUs. We pooled<br />

harvest data for each DAU from 1998-2006 because <strong>of</strong> low sample sizes and high annual<br />

variation in age and sex composition. We evaluated differences among DAUs in harvest<br />

age–sex composition using 2 age classes: subadults (kitten to 2 years old) and adults (at<br />

least 3 years old) and compared adult versus subadult proportions, proportion <strong>of</strong> females<br />

and adult females in <strong>the</strong> harvest. We evaluated differences among DAUs in age structure<br />

<strong>of</strong> harvested males using 4 age classes: kitten to 2 years old, 3 years old, 4-7 years old,<br />

and at least 8 years old. We used a subset <strong>of</strong> Warren DAU that only included wilderness<br />

units (Units 20A, 26, 27) for <strong>the</strong> comparisons <strong>of</strong> age–sex data, male ages, and <strong>the</strong><br />

proportion <strong>of</strong> female cougars in <strong>the</strong> harvest.<br />

Harvest Rate Change<br />

Since 1973, Idaho Department <strong>of</strong> Fish and Game has sustained a mandatory check <strong>of</strong><br />

harvested cougars and maintains a database that includes annual harvest numbers and sex<br />

composition by game management unit. The cougar harvest database has included age<br />

data from tooth cementum annuli since 1988. We calculated mean annual cougar harvest<br />

in Unit 26 by decade from <strong>the</strong> 1973-2006 Big Game Management Records database (B.<br />

Ackerman, Idaho Department <strong>of</strong> Fish and Game, unpublished data).<br />

In Unit 26, we compared <strong>the</strong> change in harvest levels with changes in resident cougar<br />

populations by decade over a 40-year period to assess changes in cougar harvest rate. We<br />

calculated a harvest ratio for each decade based on mean annual harvest relative to<br />

resident cougar population estimates from research. Harvest ratios were used as an index<br />

to harvest rates, because numbers <strong>of</strong> subadult and transient cougars were not known for<br />

research population estimates.<br />

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

174

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