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A comparison of sika deer population conditions between the Hidaka and Akan districts in Hokkaido, Japan

机译:日本北海道日高地区与阿寒地区的梅花鹿种群状况比较

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摘要

The sika deer (Cervus nippon yesoensis) population in Hokkaido was near threatened due to heavy snow and overexploitation for meat and fur between the 1890s and 1940s (Inukai 1952). At least three or four populations (Akan, Hidaka, Taisetsu, and Ishikari lowland) occur in the area, all of which have different mitochondrial DNA haplotype compositions and have survived a bottleneck (Nagata et al. 1998; Nabata et al. 2007). The Akan population, distributed mainly in the eastern part of Hokkaido, irrupted during the 1980s and 1990s (Kaji 1995; Uno et al. 2009). The population density estimated by aerial surveys have decreased from 1999 to 2008 in the Akan district (Uno et al. 2006; Inatomi et al. 2012). Mass mortality occurred in 1996 in Akan National Park (Uno et al. 1998) and in 1999 in Shiretoko National Park (Kaji et al. 2004), and a density effect on the recruitment rate was reported for the Akan population in the 1990s (Ueno et al. 2010). In contrast, the Hidaka population is distributed across the southwestern part of Hokkaido around the Hidaka mountain area (Nabata et al. 2007) and has increased dramatically during the 2000s (Uno et al. 2007).
机译:北海道的梅花鹿(Cervus nippon yesoensis)种群由于1890年代至1940年代之间的大雪和对肉类和毛皮的过度开采而受到威胁(Inukai 1952)。该地区至少有3或4个种群(阿寒族,日高,大雪山和石狩低地)发生,所有这些种群均具有不同的线粒体DNA单倍型组成,并且在瓶颈处幸存(Nagata等人,1998; Nabata等人,2007)。阿肯族人口主要分布在北海道东部,在1980年代和1990年代爆发(Kaji 1995; Uno等,2009)。通过航空调查估计的人口密度从1999年到2008年在阿寒地区有所下降(Uno等人2006; Inatomi等人2012)。大规模死亡发生在1996年的阿寒国家公园(Uno等人,1998年)和1999年的知床国家公园(Kaji等人2004年)中,并且在1990年代(上野)据报道阿肯族人口的招募率受到密度的影响。等(2010)。相反,日高人口分布在北海道西南部日高山区附近(Nabata等,2007),并在2000年代急剧增加(Uno等,2007)。

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