波罗的海大鸬鹚种群的自然调节:冬季严酷程度与密度依赖的相互作用

Pub Date : 2022-07-01 DOI:10.5253/arde.v109i2.a7
C. Herrmann, K. Feige, Daniel R. Otto, T. Bregnballe
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引用次数: 3

摘要

经过一段时间的持续增加和范围扩大,近年来,波罗的海大蟾蜍的数量在其大部分范围内已经稳定下来。振铃复苏表明,相当大比例的人口在可能受到长期霜冻影响的地区过冬。有证据表明,冬季的严重程度是一个重要的密度依赖性调节因素:如果人口众多,那么在严冬期间,沿海和内陆水面的冰盖会减少粮食资源的可用性,从而影响人口。然而,只要人口仍然很少,即使在非常寒冷的冬天也不会受到影响,因为剩余的可获得的粮食资源可能仍然充足。本文的分析使用德国的平均冬季温度作为波罗的海Cormorants越冬区受霜冻影响地区冬季严重程度的指标。根据丹麦、石勒苏益格-荷尔斯泰因州、梅克伦堡-西波美拉尼亚州、爱沙尼亚、芬兰和哥特兰州的年度统计,估计1980-2016年波罗的海Cormorant的数量约占总人口的50%。使用线性和非线性回归模型方法分析了冬季严重程度和密度依赖性之间的相互作用。非线性模型更好地描述了一年中波罗的海繁殖种群的规模(n)、冬季温度Tn和前一年的种群规模(n-1)之间的关系。根据该模型,即使在1882年以来有记录以来最冷的冬天,数量不到41400对的繁殖对也不会减少。1989年,波罗的海Cormorant种群首次超过严冬引起的密度依赖性调节的阈值。1995/96年的冬天是当时第一个冷到足以导致人口下降的冬天。根据该模型,在2002/2003年、2005/06年、2008/09年、2009/10年和2010/11年,冬季寒冷到足以减少人口数量。此外,该模型表明,冬季调节效应仅限于低温范围。
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Natural Regulation of the Baltic Population of the Great Cormorant Phalacrocorax carbo sinensis: The Interplay between Winter Severity and Density Dependence
After a period of continuous increase and range expansion, the Baltic Great Cormorant population has stabilised in large parts of its range in recent years. Ringing recoveries reveal that considerable proportions of the population winter in areas that can be affected by prolonged frost periods. There is evidence that winter severity is an important density-dependent regulation factor: if the population is large, ice cover of coastal and inland water surfaces during harsh winters affects the population by reducing the availability of food resources. As long as the population remained small, however, it was not affected even by very cold winters, since the remaining accessible food resources were presumably still sufficient. The analysis presented here uses the average winter temperature in Germany as a proxy for winter severity in the frost-affected parts of the wintering areas of Baltic Cormorants. The Baltic Cormorant population in 1980–2016 is estimated from annual counts in Denmark, Schleswig-Holstein, Mecklenburg-Western Pomerania, Estonia, Finland and Gotland, which account for about 50% of the total population. The interplay between winter severity and density dependence is analysed using a linear and a non-linear regression model approach. The non-linear model gives a better description of the relationship between the size of the Baltic breeding population during the year (n), the winter temperature Tn, and the population size during the previous year (n–1). According to the model, a population of less than 41,400 breeding pairs would not suffer declines during even the coldest winters recorded since 1882. In 1989, the Baltic Cormorant population exceeded for the first time the threshold value for density-dependent regulation caused by severe winters. The winter 1995/96 was then the first one cold enough to cause a population decline. According to the model, during the years 2002/2003, 2005/06, 2008/09, 2009/10 and 2010/11 the winters have been cold enough to reduce population numbers. Furthermore, the model shows that the regulative winter effect is restricted to the low temperature range.
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