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首页> 外文期刊>Hereditas >East Greenland and Barents Sea polar bears (Ursus maritimus): adaptive variation between two populations using skull morphometrics as an indicator of environmental and genetic differences
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East Greenland and Barents Sea polar bears (Ursus maritimus): adaptive variation between two populations using skull morphometrics as an indicator of environmental and genetic differences

机译:东格陵兰和巴伦支海北极熊(Ursus maritimus):两个种群之间的适​​应性变化,使用头骨形态计量学作为环境和遗传差异的指标

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摘要

The polar bears of East Greenland and those of the Barents Sea area are currently being managed as two separate management units (IUCN PBSG 2010). Paetkau et al. (1999) studied the genetic structure in 16 of the world’s 19 predefined polar bear populations, based on neutral genetic markers; very low level of genetic differentiation was found between the East Greenland and Barents Sea populations, although the allele frequency distributions qualified the two populations as separate management units (MUs) (Moritz 1994). However, recent observations have questioned the degree of separation between the two populations, suggesting a certain overlap (Born et al. 2009). Still, differences in space use (Born et al. 2009) and skull growth rates (Bechsh?ft et al. 2008a), as well as subtle differences in skull, teeth, and bone characters have been found between polar bears from East Greenland and Barents Sea (Sonne et al. 2007a, 2007b; Bechsh?ft et al. 2008b, 2009).One of the main goals of conservation genetics is the identification of evolutionary significant units (ESUs) – and MUs and the preservation of genetic diversity, which should allow the evolutionary processes of natural selection and adaptation to continue in the future. The identification of separate ESUs was originally recommended based on both ecological and genetic data, although focus has later shifted to being mainly on the assessment of neutral genetic variation (Waples 1991; deGuia and Saitoh 2007). However, a broader definition of ESUs including non-neutral markers and adaptive variation would be more appropriate (deGuia and Saitoh 2007). Neutral molecular marker loci provide only little insight into adaptive variation, unless a large fraction of the non-neutral markers are tightly linked to the relevant quantitative trait loci. Alternatively, neutral markers can provide useful information in small populations where most of the fitness variation is neutral. However, a lack of molecular divergence among populations at neutral loci is potentially uninformative, as it cannot exclude local adaptations (Lynch 1996). Neutral genetic markers such as microsatellites have a well-known inheritance but may not be useful in studies of local adaptation, since there is often a limited correlation between neutral and selective variation in natural populations (Meril? and Crnokrak 2001). Genetic differences, on the other hand, could potentially be measured by proxy instead, as e.g. morphometric variation in physical traits.Knowledge of local adaptation and adaptive potential of various wildlife populations is becoming increasingly relevant due to impacts on the environment from i.e. climate change and pollution, which could potentially favour the more adaptive species. Divergent natural selection due to spatially varying environments is expected to promote adaptive evolutionary responses (Kawecki and Ebert 2004). Hence, the evolutionary outcome is dictated by the relative strength of natural selection (Endler 1986).Selective forces influence populations in various parts of their range differently (Andersson 1994). Demonstration that a population is adapted to a given environment is also important (Pertoldi et al. 2007, 2009). Acquiring direct evidence involves either comparison of fitness among populations in local and foreign environments (Kawecki and Ebert 2004).Presently more information is thus wanted on the degree of exchange between the polar bear populations of East Greenland and the Barents Sea. The main aim of the present study was therefore to compare differences in size and shape of East Greenland and Barents Sea polar bear skulls, exploring the degree of morphometric differentiation between the two populations.
机译:东格陵兰岛和巴伦支海地区的北极熊目前作为两个独立的管理单位进行管理(IUCN PBSG 2010)。 Paetkau等。 (1999)基于中性遗传标记研究了世界上19个预定的北极熊种群中16个的遗传结构。尽管等位基因频率分布使两个种群成为单独的管理单位(MUs),但在东格陵兰岛和巴伦支海种群之间发现的遗传分化水平非常低(Moritz 1994)。但是,最近的观察对两个种群之间的分离程度提出了质疑,表明存在一定的重叠性(Born等,2009)。尽管如此,在东格陵兰岛和北极熊之间发现了空间利用的差异(Born等,2009)和头骨的生长速率(Bechsh?ft等,2008a),以及头骨,牙齿和骨骼的细微差别。巴伦支海(Sonne et al。2007a,2007b; Bechsh?ft et al。2008b,2009)。保护遗传学的主要目标之一是确定进化重要单位(ESUs)和MUs,并保护遗传多样性,这将使自然选择和适应的进化过程在未来得以继续。最初建议基于生态和遗传数据来鉴定单独的ESU,尽管后来的重点已转移到主要针对中性遗传变异的评估(Waples 1991; deGuia和Saitoh 2007)。但是,对ESU进行更广泛的定义(包括非中性标记和适应性变异)将更为合适(deGuia和Saitoh 2007)。中性分子标记基因座只能提供很少的适应性变化见识,除非很大一部分非中性标记物与相关的数量性状基因座紧密相连。另外,中性标记可以在大多数适应度变化为中性的小人群中提供有用的信息。但是,在中性位点的人群之间缺乏分子差异可能是无意义的,因为它不能排除局部适应性的影响(Lynch 1996)。中性遗传标记(例如微卫星)具有众所周知的遗传,但可能不适用于局部适应性研究,因为自然种群中的中性和选择性变异之间通常存在有限的相关性(Meril?和Crnokrak 2001)。另一方面,遗传差异可能可以通过代理来衡量,例如由于气候变化和污染对环境的影响,各种野生动植物种群对当地适应和适应潜力的认识与日俱增,这可能有利于适应性更强的物种。预期由于空间变化环境而产生的自然选择会促进适应性进化反应(Kawecki和Ebert 2004)。因此,进化的结果取决于自然选择的相对强度(Endler 1986)。选择力对范围内各个部分的人口的影响不同(Andersson 1994)。证明人口适应给定环境也很重要(Pertoldi等,2007,2009)。获取直接证据需要比较本地和国外环境中种群之间的适​​应度(Kawecki和Ebert,2004年)。因此,目前需要更多有关东格陵兰岛和巴伦支海的北极熊种群之间交换程度的信息。因此,本研究的主要目的是比较东格陵兰岛和巴伦支海北极熊头骨的大小和形状的差异,探索两个种群之间的形态学分化程度。

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