Performance of Juvenile Cutthroat Trout Translocated as Embryos from Five Populations into a Common Habitat
- Andrews, Tessa C [ Montana State University: Ecology ]
- Shepard, Bradley B [ Montana Fish, Wildlife, and Parks, Post Office Box 200701, Helena, Montana 59620, USA ]
- Litt, Andrea R [ Montana State University: Ecology ]
- Kruse, Carter G [ Turner Enterprises, Inc., 901 Technology Boulevard, Bozeman, MT 59718, USA ]
- Nelson, M Lee [ Montana Fish, Wildlife an Parks, 1420 East 6th, Helena, MT 59620, USA ]
- Clancey, Patrick [ Montana Fish, Wildlife and Parks, Post Office Box 1336, Ennis, Montana 59729, USA ]
- Zale, Alexander V [ U.S. Geological Survey, Montana Cooperative Fishery Research Unit, Montana State University, Post Office Box 173460, Bozeman, Montana 59717, USA ]
- Taper, Mark L [ Montana State University: Ecology ]
- Kalinowski, Steven T [ Montana State University: Ecology ]
The distributions of most native trout species in western North America have been severely reduced, and conservation of many of these species will require translocation into vacant habitats following removal of nonnative species. A critical question managers have is "Does it matter which donor sources are used for these translocations?" We present a case study that addressed this question for a large native trout translocation project in Montana. We introduced embryos from five source populations of Westslope Cutthroat Trout Oncorhynchus clarkii lewisi to a large, fishless watershed in Montana following removal of nonnative fish with piscicides. Source populations providing embryos for translocations were three nearby (< 120 km) wild populations, the state of Montana's captive Westslope Cutthroat Trout hatchery conservation population (initiated 32 years ago using fish from wild populations located > 350 km from the translocation site), and a population in captivity for one generation comprised of individuals from the three wild populations used as single sources for this project, which were variably crossed (59% within populations and 41% between populations) to provide embryos. We used remote-site incubators at six different sites to introduce approximately 35,000 embryos from 400 genotyped parents. We later resampled and genotyped 1,450 of these individuals at age 1 and age 2. Juvenile survival for the more genetically diverse Montana Westslope Cutthroat Trout conservation population was twice as high as for other source populations, even though these other source populations were geographically closer to the translocation site than populations used to make the Montana Westslope Cutthroat Trout conservation population. Body weight for progeny from the two captive populations was higher than for progeny from wild source populations, and some differences were observed in body condition among source populations. Continued monitoring over several generations will be necessary to determine the eventual contributions of each source population and the relevance of these initial findings.