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Reintroduction of the lynx into the Vosges mountain massif: From animal survival and movements to population development

机译:将山猫重新引入孚日山脉:从动物的生存和运动到种群发展

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The factors related to successful reintroduction campaigns of lynx (Lynx lynx, Linné 1758) in Europe may be identified from monitoring programs, such as the one implemented in France since the first releases that took place in 1983. We studied survival and movements of the released animals using telemetry. We estimated the population’s expansion from the data obtained by a spatial analysis of 616 indices of lynx presence collected between 1988 and 2002, and roughly compared these to the ones givenby a simulation of the theoretical development of this population obtained by a stochastic population model. After their release, the lynx roamed (over 5.4- to 36.9-km) around the site of release so that, within the first three months, the mean prospected area averaged 236 km~2 (84–566 km~2). Of the 21 reintroduced lynx, 4 females and 6 males were able to survive and so contributed to the population's establishment. The lynx distribution area covered 1872 km~2 in 1988–1990 and increased to 3159 km~2 in 2000–2002. The area’s expansion most often started in the reintroduction sites where, as of 1987, the first cases of reproduction were recorded. Such population development could only be simulated with rather high adult survival rates. The small surface area occupied by a permanent population core (1962 km~2) and the long time needed to settle down, could then be due to the small number of founders, to the fact that for 10 years the releases had been spaced out and because, from a demographic pointof view, the resultant population was isolated from other possible source-populations of lynx. Twenty years later, and relative to other lynx population cores in France (e.g. the one in the Jura), the status of the lynx in the Vosges mountain massif is still uncertain: there, the lynx is still expanding its distribution area and may establish itself throughout the Vosges massif provided that the current increase in its population numbers will not fall back again (e.g. no increase in human-related mortality).
机译:可以从监测计划中确定与欧洲(Lynx lynx,Linné1758)成功重新引入运动有关的因素,例如自1983年首次发布以来在法国实施的一项计划。我们研究了该释放物的存活和运动动物使用遥测技术。我们通过对1988年至2002年收集的616个的存在进行空间分析而获得的数据,估计了人口的扩张,并将这些与通过随机人口模型获得的对该人口理论发展的模拟所得出的结果进行了粗略的比较。 their被释放后,the在释放点周围漫游(超过5.4至36.9 km),因此,在头三个月内,平均勘探面积平均为236 km〜2(84–566 km〜2)。在重新引入的21只山猫中,有4头雌性和6头雄性能够存活,因此为种群的建立做出了贡献。的分布面积在1988–1990年覆盖1872 km〜2,在2000–2002年增加到3159 km〜2。该地区的扩张通常始于重新引入的地点,从1987年开始记录了第一批繁殖病例。只能以相当高的成年存活率模拟这种人口发展。一个永久人口核心所占的表面积很小(1962 km〜2),并且需要很长时间才能安定下来,这可能是由于创始人人数少,发行已经间隔了10年并且因为从人口统计学的角度来看,所得的种群与山猫的其他可能的源种群是隔离的。二十年后,相对于法国的其他山猫种群核心地区(例如朱拉地区),山猫在孚日山脉地块中的地位仍然不确定:在那里,山猫仍在扩大其分布范围并可能建立自己的地位在整个孚日山脉,前提是目前的人口数量不会再回落(例如,与人类有关的死亡率不会增加)。

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