首页> 外文期刊>Forest Ecology and Management >Demographic changes in a Scottish red deer population (Cervus elaphus L.) in response to sustained and heavy culling: an analysis of trends in deer populations of Creag Meagaidh National Nature Reserve 1986-2001.
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Demographic changes in a Scottish red deer population (Cervus elaphus L.) in response to sustained and heavy culling: an analysis of trends in deer populations of Creag Meagaidh National Nature Reserve 1986-2001.

机译:苏格兰马鹿种群(Cervus elaphus L.)响应持续和繁重的扑杀而发生的人口变化:Creag Meagaidh国家自然保护区1986-2001年鹿种群趋势的分析。

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From the time of its designation as a National Nature Reserve in 1986, declared policy at Creag Meagaidh NNR has been to reduce populations of sheep and native red deer to levels compatible with achieving the active regeneration of native birch woodland. Sheep grazing has been removed from the Reserve area, and deer populations subject to reduction through culling and live sale. Regular monitoring of both vegetation and deer populations has been maintained since the Reserve was established, with detailed records kept of number of deers (and sheep) recorded on the Reserve in regular counts (monthly since 1992). Records are also maintained of the number of deer culled, together with details of age, sex, weights and reproductive status. These data are examined in order to explore the effects of a sustained reduction of overall density on the demography and performance of a Highland red deer population. It is clear that despite a heavy and sustained culling pressure on red deer populations of Creag Meagaidh, the Reserve area still supports a significant population of animals. Although numbers on the Reserve initially showed a significant decline until the mid-1990s, observations of animals using the Reserve area have subsequently increased once more to levels approaching those of the mid-1980s. There is however marked (diurnal and) seasonal variation in number of animals recorded on the Reserve and it would appear that current usage is largely by transient individuals or relatively recent immigrants. While significant differences in carcase weight were observed between male and female calves, no differences across years were determined for calves, adult or yearling stags. A significant change in weights of adult hinds was however apparent through 1992 and 1993 resulting in a stepwise increase between weights of the periods 1988-1992 and 1994-2000. Consistent data on lactational status and pregnancy of hinds culled are available only from 1992. The overall proportions of milk and yeld hinds in the culled population has shown no significant change between 1994 and 2000. Although there is some suggestion of an increase in the overall proportion of milk hinds between 1992 and 1993 and the years after 1994 (milk hinds as proportion of all hinds shot) data are insufficient to test whether this is a statistically significant trend, or merely year-to-year variation. There is further no evidence of a consistent difference in rates of pregnancy between animals classified as lactating or yeld at time of death. Overall some 77.9% of yeld animals and 74.4% of milk animals were recorded with foetuses. Finally, over the period for which data are available (1992-2000) there is no evidence of a consistent change in time in the proportion of mature animals found pregnant and recruitment rates (as number of surviving calves counted in late winter per 100 hinds) have averaged at approximately 0.39 or 39 calves per 100 hinds. Given the efforts made to reduce population size and maintain deer at low density, such a lack of response in recorded body weights or fecundity is perhaps unexpected. However, accepting the composition of the Reserve's deer present population (reduced to a resident herd of minimal size and composed primarily of transients which are in practice spending only a relatively small part of their time visiting the Reserve), perhaps the lack of clarity in demographic traits is not unduly surprising. We are not documenting in practice changes in any residual, original population following some reduction of density, but rather in recent or even temporary immigrants. The implications of these conclusions for population management, and the effects of the sustained culling operations at Creag Meagaidh on the deer populations within neighbouring Estates are explored; some comparisons are made with preliminary results emerging from a similar exercise in reducing deer population density and browsing pressure at the RSPB's Abernethy Reserve.
机译:从1986年被指定为国家级自然保护区以来,Creag Meagaidh NNR宣布的政策一直是将绵羊和本地马鹿的种群减少到与实现本地桦木林地的主动更新相适应的水平。绵羊放牧已从保护区中撤出,鹿的数量通过淘汰和现场出售而减少。自保护区建立以来,对植被和鹿种群进行了定期监测,并定期记录了保护区记录的鹿(和绵羊)数量的详细记录(自1992年以来每月)。还记录了被淘汰的鹿的数量,以及年龄,性别,体重和生殖状况的详细信息。检查这些数据是为了探索持续降低总体密度对高地红鹿种群的人口统计学和性能的影响。显然,尽管对Creag Meagaidh的马鹿种群造成了沉重而持续的淘汰压力,但保护区仍支持大量动物。尽管保护区的数量最初显示出明显的下降,直到1990年代中期,但使用保护区的动物观测值随后又增加到接近1980年代中期的水平。但是,保护区上记录的动物数量有明显的(昼夜和季节性)变化,而且当前的使用似乎主要是由暂住的个体或相对较新的移民所致。虽然观察到雄性和雌性小牛的car体重量有显着差异,但对于小牛,成年或一岁的雄鹿来说,多年来没有发现差异。然而,到1992年和1993年,成年后足重量的显着变化是明显的,导致1988-1992年和1994-2000年之间的重量逐渐增加。仅可从1992年获得有关哺乳后代和哺乳后代的妊娠的一致数据。在被淘汰的人群中,牛奶和产后代的总比例在1994年至2000年之间没有显着变化。尽管有人暗示总体比例会增加在1992年至1993年至1994年之后的数年中,牛奶后代(牛奶后代占所有后代射击的比例)数据不足以检验这是统计上的显着趋势还是仅仅是逐年变化。进一步没有证据表明在死亡时被分类为哺乳期或产量的动物之间的妊娠率存在一致的差异。总体上,约有77.9%的产量动物和74.4%的乳动物记录有胎儿。最后,在可获得数据的时期(1992年至2000年),没有证据表明怀孕的成年动物的比例和招募率随时间持续变化(以每100个后代在冬末计数的存活小牛数)。平均每100个后代约有0.39或39个犊牛。考虑到为减少种群规模和将鹿维持在低密度而做出的努力,在记录的体重或繁殖力方面缺乏反应可能是意料之外的。但是,接受保护区鹿群现有种群的组成(减少到最小的居民群,并且主要由瞬态组成,实际上他们只花很少一部分时间访问保护区),也许在人口统计上缺乏明确性特质不足为奇。在实践中,我们没有记录密度降低后残留的任何原始人口的变化,而是最近或什至是临时移民的变化。探讨了这些结论对人口管理的影响,以及在Creag Meagaidh持续进行的扑杀行动对邻近屋村内鹿种群的影响;进行了一些比较,并得出了类似的初步结果,这些结果是通过减少RSPB的Abernethy保护区的鹿群密度和浏览压力来进行的。

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