Northern Rockies Conservation Cooperative, Jackson, Wyoming, United States of America.
Department of Environmental Conservation, University of Massachusetts Amherst, Amherst, Massachusetts, United States of America.
PLoS One. 2020 May 29;15(5):e0233726. doi: 10.1371/journal.pone.0233726. eCollection 2020.
Whitebark pine (Pinus albicaulis), a keystone species and an obligate mutualist of the Clark's nutcracker (Nucifraga columbiana), is rapidly declining throughout its range. Evidence suggests this decline is leading to a downward trend in local nutcracker populations, which would in-turn decrease whitebark pine regeneration. Our objectives were to (1) evaluate temporal variation in nutcracker habitat use as a function of whitebark pine and Douglas-fir (Pseudotsuga menziesii) habitat, at local and landscape scales, (2) develop metrics for predicting when whitebark pine communities require intervention to sustain nutcracker visitation, and (3) test McKinney et al. (2009) and Barringer et al.'s (2012) models predicting nutcracker occurrence. Between 2009 and 2013, we carried out 3,135 audio-visual Clark's nutcracker surveys at 238 random points in the southern Greater Yellowstone Ecosystem. Using Bayesian occupancy models and cross-product model selection, we evaluated the association between nutcracker occurrence and habitat variables during five stages of the nutcracker annual cycle, while accounting for imperfect detection. Nutcracker occurrence was most strongly associated with the presence of cone-bearing whitebark pine trees (rather than cone density) and the area of whitebark pine on the landscape. To promote a high, >75%, probability of occurrence at a site within the study area, we recommend a management plan that achieves a landscape composed of a minimum of 12,500-25,000 ha of cone-bearing whitebark pine habitat within a 32.6 km radius. Additionally, an optimal habitat mosaic includes moderate levels of Douglas-fir habitat. Models currently used to guide whitebark pine management strategies underpredicted nutcracker occurrence in our study area, suggesting these strategies may not be appropriate in the region. We cannot predict how this mutualistic relationship will change as the population density of each species shifts. We therefore suggest conducting periodic surveys to re-evaluate the relationship as the environment changes and management strategies are implemented.
白皮松(Pinus albicaulis)是一种关键物种,也是黑啄木鸟(Nucifraga columbiana)的专性共生种,其分布范围正在迅速缩小。有证据表明,这种衰退导致了当地黑啄木鸟数量的下降趋势,这反过来又会减少白皮松的再生。我们的目标是:(1) 评估黑啄木鸟栖息地利用随白皮松和花旗松(Pseudotsuga menziesii)栖息地的时间变化,在局部和景观尺度上;(2) 制定预测白皮松群落何时需要干预以维持黑啄木鸟访问的指标;(3) 测试 McKinney 等人(2009)和 Barringer 等人(2012)预测黑啄木鸟出现的模型。2009 年至 2013 年,我们在大黄石南部生态系统的 238 个随机点进行了 3135 次黑啄木鸟视听调查。使用贝叶斯占有率模型和交叉乘积模型选择,我们评估了在黑啄木鸟年度周期的五个阶段中,黑啄木鸟出现与栖息地变量之间的关系,同时考虑了不完全检测。黑啄木鸟的出现与有球果的白皮松树的存在(而不是球果密度)和景观上白皮松的面积最密切相关。为了在研究区域内的一个地点提高出现概率 >75%,我们建议制定一个管理计划,该计划在 32.6 公里半径范围内实现由至少 12500-25000 公顷有球果的白皮松栖息地组成的景观。此外,一个最佳的栖息地镶嵌体包括中等水平的花旗松栖息地。在我们的研究区域中,目前用于指导白皮松管理策略的模型低估了黑啄木鸟的出现,这表明这些策略在该地区可能不合适。我们无法预测随着每个物种的种群密度变化,这种共生关系将如何变化。因此,我们建议定期进行调查,以在环境变化和实施管理策略时重新评估这种关系。