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Proceedings of the fifth mountain lion workshop: 27

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92 PROCEEDINGS OF THE FIFTH MOUNTAIN LION WORKSHOP<br />

IN THE PENINSULAR RANGES OF CALIFORNIA<br />

Es<strong>the</strong>r Rubin. Department <strong>of</strong> Pathology, Microbiology, and Immunology, School <strong>of</strong> Veterinary Medicine, University <strong>of</strong><br />

California, Davis, CA 95616, USA<br />

Walter Boyce. Department <strong>of</strong> Pathology, Microbiology, and Immunology, School <strong>of</strong> Veterinary Medicine, University <strong>of</strong><br />

California, Davis, CA 95616, USA<br />

Charles Hayes. Department <strong>of</strong> Pathology, Microbiology, and Immunology, School <strong>of</strong> Veterinary Medicine, University <strong>of</strong><br />

California, Davis, CA 95616, USA<br />

Steve Torres. California Department <strong>of</strong> Fish and Game, 1416 Ninth Street, Sacramento, CA 95814, USA.<br />

Mark Jorgensen. Anza Borrego Desert State Park, 200 Palm Canyon Drive, Borrego Springs, CA 92004, USA.<br />

An investigation <strong>of</strong> cause-specific mortality among 91 radio collared bighorn sheep was conducted from November<br />

1992 through January 1996 in <strong>the</strong> Peninsular Ranges <strong>of</strong> sou<strong>the</strong>rn California. Mountain <strong>lion</strong> predation was <strong>the</strong> most<br />

significant cause <strong>of</strong> mortality and accounted for 63% (<strong>27</strong>/43) <strong>of</strong> all mortalities in <strong>the</strong> 6 sheep populations included in <strong>the</strong><br />

study. Lions accounted for 0-100% <strong>of</strong> all mortalities within <strong>the</strong>se populations, and 0-<strong>27</strong>% <strong>of</strong> <strong>the</strong> radio collared sheep within<br />

any given population were killed by <strong>lion</strong>s annually. The age at capture <strong>of</strong> <strong>the</strong> sheep varied significantly among populations,<br />

and <strong>the</strong> age distribution <strong>of</strong> sheep killed by <strong>lion</strong>s did not appear to differ from this pattern. Sheep <strong>of</strong> both sexes were preyed<br />

upon by <strong>lion</strong>s but a statistical comparison between sexes was not possible because only a small number <strong>of</strong> rams were radio<br />

collared. Predation occurred during all times <strong>of</strong> <strong>the</strong> year except for <strong>the</strong> months <strong>of</strong> June, July, and August. Sixty-seven<br />

percent (18/<strong>27</strong>) <strong>of</strong> <strong>the</strong> predation events occurred between December and March. It appears that <strong>lion</strong> predation has been a<br />

significant limiting factor during <strong>the</strong> past three years, and sustained high levels <strong>of</strong> predation by <strong>lion</strong>s may adversely affect <strong>the</strong><br />

long-term viability <strong>of</strong> this threatened metapopulation <strong>of</strong> bighorn sheep.<br />

ORIENTATION, MOVEMENTS, AND SURVIVAL OF TRANSLOCATED<br />

COUGARS IN NEW MEXICO<br />

T.K. Ruth. Hornocker Wildlife Institute, Moscow, ID 83843, USA.<br />

K.A. Logan. Hornocker Wildlife Institute, Moscow, ID 83843, USA.<br />

L.L. Sweanor. Hornocker Wildlife Institute, Moscow, ID 83843, USA.<br />

M.G. Hornocker. Hornocker Wildlife Institute, Moscow, ID 83843, USA.<br />

L.J. Temple. New Mexico Department <strong>of</strong> Game and Fish, 87714, USA.<br />

We conducted a 2-year study <strong>of</strong> wild-caught translocated cougars to evaluate translocation as a management tool to:<br />

1) re-establish cougar populations in historic ranges, 2) relieve <strong>the</strong> threat <strong>of</strong> inbreeding in isolated populations, and 3)<br />

manage nuisance cougars. Our objectives were to document orientation, movements, establishment, and survival <strong>of</strong><br />

translocated cougars and to make comparisons with similar parameters for cougars in a reference population. Thirteen<br />

cougars were translocated an average <strong>of</strong> 477 km from <strong>the</strong> San Andres Mountains (SAM) study area in south-central New<br />

Mexico to 9 release sites in nor<strong>the</strong>astern New Mexico and were monitored from 9 December 1990 through 7 January 1993.<br />

A fourteenth cougar was translocated 338 km from <strong>the</strong> SAM to northwestern New Mexico on 8 April 1989 and monitored to<br />

29 May 1990. Initial orientation <strong>of</strong> cougars away from release sites ranged from 22E-313E and were uniformly distributed<br />

about a 360E circle. Eight (4 M:4 F) <strong>of</strong> 14 cougars had endpoints > 80 km from <strong>the</strong>ir release sites and endpoint directions<br />

that were almost exclusively south, southwest or sou<strong>the</strong>ast (x=181E), suggesting <strong>the</strong> cougars homed toward <strong>the</strong> source<br />

population. Two males returned to <strong>the</strong>ir original home ranges in <strong>the</strong> SAM. Distances moved from release sites to endpoints<br />

ranged from 3-285 km for 8 females and 11-494 km for 6 males. Nine <strong>of</strong> 14 translocated cougars died during <strong>the</strong> study.<br />

Annual survival rates for translocated cougars averaged 0.55 for females and 0.44 for males and were lower for both sexes<br />

during <strong>the</strong> second year <strong>of</strong> <strong>the</strong> study. Translocation was most successful with cougars that were 12-<strong>27</strong> months <strong>of</strong> age. For<br />

management or conservation programs, we suggest that 12-<strong>27</strong> month-old cougars are <strong>the</strong> best candidates for translocation.

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