金雕栖息地的特征和变化

Diversity Pub Date : 2024-08-31 DOI:10.3390/d16090523
Alan H. Fielding, David Anderson, Catherine Barlow, Stuart Benn, Charlotte J. Chandler, Robin Reid, Ruth Tingay, Ewan D. Weston, D. Philip Whitfield
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引用次数: 0

摘要

通过卫星跟踪可以对金雕的家园范围特征进行新颖的调查。了解家域特征对于保护和评估植树造林、风电场等景观变化的潜在影响非常重要。小样本量、不一致的定义和方法限制了之前的一些研究。我们的研究涉及苏格兰五个地区的 69 只被标记的鹰,数据采集时间超过一年。根据从利用率分布中提取的 95% 等距等值线估算了家园范围的大小。在一个较小的临界值以上,估计的活动范围大小不受记录数量的影响,但至少需要一年的数据,这主要是因为繁殖期和非繁殖期的季节性差异。被标记为活动范围保持者的鸟类与之前被标记为雏鸟的鸟类之间没有明显的活动范围大小差异。在区域内差异较大的四个地区,95%的平面等值线没有差异(中位数,平方公里):阿盖尔 58.9、西北高地 61.7、东北高地 89.3、苏格兰南部 91.9。与世隔绝的外赫布里底群岛地区的分布区特别小,只有 24.0 平方公里。根据金雕地形(GET)模型的估算,当局限于可用栖息地时,估计的分布区面积通常会减少到平面面积的 70-80%。采用已知的不适宜栖息地(郁闭树冠的商业森林和风力涡轮机)的措施进一步减少了可利用的空地。商业森林造成了大量原本适宜的栖息地丧失。范围越大,适宜栖息地的范围就越大(根据 GET),GET 首选栖息地的最佳范围并不明显。在不同年份,雌雄的活动范围大小没有差异。繁殖期的范围较小,雌性的繁殖范围远小于雄性,但在非繁殖期的范围大于雄性。繁殖尝试的持续时间可能也有影响。我们的研究为了解金雕的巢域特征提供了新的视角,可以指导进一步的研究和实际应用。
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The Characteristics and Variation of the Golden Eagle Aquila chrysaetos Home Range
Satellite tracking allows for novel investigations into golden eagle home range characteristics. Understanding home range characteristics is important for conservation and for assessing the potential impact of landscape changes from forest planting, wind farms, etc. Small sample sizes, inconsistent definitions and methods restricted several previous studies. Our study involved 69 resident tagged eagles with over one year of data across five Scottish regions. Home range size was estimated from 95% isopleth contours extracted from Utilisation Distributions. Above a small threshold, estimated range size was not affected by the number of records but at least one year of data is required, largely because of the breeding and non-breeding seasonal differences. There were no significant range size differences between birds tagged as range holders and those previously tagged as nestlings. Across four regions, with considerable intra-regional variation, planar 95% isopleths did not differ (medians, km2): Argyll 58.9, Northwest Highlands 61.7, Northeast Highlands 89.3, South of Scotland 91.9. Ranges in the isolated Outer Hebrides region were exceptionally small, at 24.0 km2. Estimated range area was usually reduced to 70–80% of the planar area when restricted to usable habitat, as estimated by the Golden Eagle Topography (GET) model. Applying measures of known unsuitable habitat (closed-canopy commercial forest and wind turbines) further reduced usable open land. Loss of otherwise suitable habitat was substantially due to commercial forest. Larger ranges had larger extents of suitable habitat (according to GET), with no apparent optimum of preferred GET habitat. Range size was not different across a year between the sexes. Breeding ranges were smaller, and females’ breeding ranges were much smaller than those of males, but larger than males’ ranges in the non-breeding season. Breeding attempt duration was probably also influential. Our study provides novel insights into golden eagle home range characteristics and can guide further research and practical applications.
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