Hebblewhite Mark, Merrill Evelyn H
Wildlife Biology Program, Department of Ecosystem and Conservation Sciences, College of Forestry, University of Montana, Missoula, MT 59812, USA.
Oecologia. 2007 May;152(2):377-87. doi: 10.1007/s00442-007-0661-y. Epub 2007 Feb 8.
While migration is hypothesized to reduce predation risk for ungulates, there have been few direct empirical tests of this hypothesis. Furthermore, few studies examined multiscale predation risk avoidance by migrant ungulates, yet recent research reveals that predator-prey interactions occur at multiple scales. We test the predation risk reduction hypothesis at two spatial scales in a partially migratory elk (Cervus elaphus) population by comparing exposure of migrant and resident elk to wolf (Canis lupus) predation risk. We used GPS and VHF telemetry data collected from 67 migrant and 44 resident elk over the summers of 2002-2004 in and adjacent to Banff National Park (BNP), Canada. We used wolf GPS and VHF telemetry data to estimate predation risk as a function of the relative probability of wolf occurrence weighted by a spatial density model that adjusted for varying pack sizes. We validated the predation risk model using independent data on wolf-killed elk, and showed that combining wolf presence and spatial density best predicted where an elk was likely to be killed. Predation risk on summer ranges of migrant elk was reduced by 70% compared to within resident elk summer ranges. Because wolves avoided areas near high human activity, however, fine-scale selection by resident elk for areas near high human activity reduced their predation risk exposure to only 15% higher than migrants, a difference significant in only one of three summers. Finally, during actual migration, elk were exposed to 1.7 times more predation risk than residents, even though migration was rapid. Our results support the hypothesis that large-scale migrations can reduce predation. However, we also show that where small-scale spatial variation in predation risk exists, nonmigratory elk may equally reduce predation risk as effectively as migrants under some circumstances.
虽然有假说认为迁徙能降低有蹄类动物被捕食的风险,但对这一假说的直接实证检验却很少。此外,很少有研究考察迁徙有蹄类动物在多尺度上对被捕食风险的规避情况,然而最近的研究表明,捕食者与猎物的相互作用发生在多个尺度上。我们通过比较迁徙和留居的驼鹿( Cervus elaphus )暴露于狼( Canis lupus )捕食风险的情况,在一个部分迁徙的驼鹿种群中,于两个空间尺度上检验捕食风险降低假说。我们使用了2002 - 2004年夏季在加拿大班夫国家公园(BNP)及其周边收集的67只迁徙驼鹿和44只留居驼鹿的GPS和甚高频遥测数据。我们利用狼的GPS和甚高频遥测数据,通过一个根据狼群大小变化进行调整的空间密度模型加权计算狼出现的相对概率,来估计捕食风险。我们利用狼捕杀驼鹿的独立数据验证了捕食风险模型,并表明结合狼的存在和空间密度能最好地预测驼鹿可能被杀死的地点。与留居驼鹿的夏季活动范围相比,迁徙驼鹿夏季活动范围内的捕食风险降低了70%。然而,由于狼会避开人类活动频繁的区域,留居驼鹿对人类活动频繁区域的精细尺度选择使得它们面临的捕食风险仅比迁徙驼鹿高15%,且这种差异仅在三个夏季中的一个夏季显著。最后,在实际迁徙过程中,尽管迁徙速度很快,但驼鹿面临的捕食风险是留居驼鹿的1.7倍。我们的结果支持了大规模迁徙能降低被捕食风险的假说。然而,我们也表明,在存在捕食风险的小尺度空间变化的情况下,在某些情况下,非迁徙驼鹿可能与迁徙驼鹿一样有效地降低捕食风险。