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首页> 外文期刊>Hereditas >Influence of spatial structure on genetic isolation in Plebejus argus populations (Lepidoptera: Lycaenidae)
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Influence of spatial structure on genetic isolation in Plebejus argus populations (Lepidoptera: Lycaenidae)

机译:空间结构对斑节菜种群遗传分离的影响(鳞翅目:盲蛾科)

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In industrialized countries natural habitats both decrease in abundance and increase in their patchiness. The isolation of habitat patches from each other is a major cause of long term decline of many species. For non-migratory butterflies, the recolonization of previously occupied habitats depends on the proximity to occupied patches (Thomas and Jones 1993). Populations of widely distributed species with limited dispersal abilities seem to be particularly at risk from an increased fragmentation, as these have suffered more from an increased fragmentation than more vagile species (Maes and VanDyck 2001). The severe decline of many butterfly species in northwest Europe is partly due to an increased fragmentation of their habitats (vanSwaay and Warren 1999).In order to assess the impact of habitat fragmentation of populations, one should compare situations where the distribution of a species is naturally patchy with an area where the species has a more continuous habitat. The silver-studded blue Plebejus argus is a Lycaenid butterfly widely distributed in Europe. It may be locally abundant within its distribution range and is usually patchily distributed in Britain, where it has been intensively studied (Thomas 1985, Thomas 1996; Brookes et al. 1997; Lewis et al. 1997; Thomas et al. 1998). British populations show very limited dispersal abilities, resulting in mostly closed population structure. In other parts of Europe, the situation is quite different: in SW Spain, the species habitat is fairly continuous throughout the Do?ana National park, where Halimium halimifolium, its local food plant, is abundant. The density of P. argus is also dependent upon the density of Lasius niger, its obligatory host ant species (Jordano et al. 1992; Seymour and Jordano pers. comm.). In southern Finland, the species is present in numerous islets in the Baltic Sea, which may naturally have very small habitat patches. We hypothesize that the dispersal ability of this species may vary within its European range. On one hand, individuals from the most continuous habitats (i.e. in the Do?ana N.P.) may disperse more than in naturally fragmented habitats, as they would be under less selection pressure against dispersal. On the other hand, in Finland, individuals on islands may be selected against dispersal, resulting in isolated populations. These islands must have been colonised by individuals crossing the sea, hence there is a possibility for an evolution of high dispersal abilities in a few individuals, resulting in a dual strategy of sedentarity and dispersal. This may depend on genotype and ecological and behavioural conditions (Ims and Hjermann 2001). The aim of this study is to investigate dispersal from the point of view of its consequences on the genetic population structure of populations. Basically there can be three main possible spatial structures of population differentiation. (1) If populations show a marked isolation-by-distance effect, dispersal occurs locally in a stepping stone manner, most dispersing individuals moving only between neighbouring habitat patches. (2) If populations are not genetically different from each other, then there is a high rate of dispersal, even between population far away from each other, resulting in a regional panmixia. (3) If populations are genetically different from each other but do not show isolation by distance effect, this may be due to occasional long distance colonisation where genetic differences occur due to founder effect. The aim of the present study is to identify the population structure of Plebejus argus in two contrasted landscape structures: the rather continuous habitat of Do?ana National Park with the naturally patchily distributed populations of forest clearings and islands in south Finland.
机译:在工业化国家中,自然栖息地的丰富度和斑块性都有所增加。生境斑块彼此隔离是许多物种长期衰退的主要原因。对于非迁移性蝴蝶,先前被占领的栖息地的重新定殖取决于与被占领斑块的接近程度(Thomas and Jones 1993)。分散能力有限的广泛分布物种的种群似乎特别容易受到碎片化的威胁,因为与更多易变的物种相比,碎片化增加的影响更大(Maes and VanDyck 2001)。西北欧许多蝴蝶物种的严重减少部分是由于其栖息地碎片化程度的增加(vanSwaay and Warren 1999)。为了评估种群栖息地碎片化的影响,人们应该比较一个物种分布情况。在该物种具有更连续栖息地的区域自然斑驳。银色点缀的蓝色Plebejus argus是在欧洲广泛分布的Lycaenid蝴蝶。它可能在其分布范围内局部丰富,通常在英国进行了广泛的研究(英国,托马斯,1985;托马斯,1996;布鲁克斯等,1997;刘易斯等,1997;托马斯等,1998)。英国人口的分散能力非常有限,导致人口结构基本封闭。在欧洲其他地区,情况则大不相同:在西班牙西南部,整个Do?ana国家公园的物种栖息地都相当连续,当地的食用植物Halimium halimifolium丰富。阿氏假单胞菌的密度还取决于其必不可少的寄主蚂蚁物种黑松鼠的密度(Jordano等,1992; Seymour和Jordano pers。comm。)。在芬兰南部,该物种存在于波罗的海的众多小岛中,这些小岛自然可能只有很小的栖息地。我们假设该物种的扩散能力可能在其欧洲范围内变化。一方面,来自最连续栖息地(即在Do?ana N.P.)的个体比自然零散的栖息地散布更多,因为他们承受的选择压力较小。另一方面,在芬兰,可能会选择反对扩散的岛屿上的个人,导致人口孤立。这些岛屿一定是由过海的个人殖民的,因此有可能在少数个人中发展高度分散的能力,从而导致久坐与分散的双重战略。这可能取决于基因型以及生态和行为条件(Ims和Hjermann 2001)。这项研究的目的是从扩散对人口遗传种群结构的影响的角度进行研究。基本上,可能存在三种主要的人口分化空间结构。 (1)如果种群表现出显着的远距离隔离效应,则散布以踏脚石的方式局部发生,大多数散布的个体仅在相邻生境斑块之间移动。 (2)如果种群之间在遗传上没有差异,那么即使在彼此相距较远的种群之间也存在很高的分散速度,从而导致区域性混杂症。 (3)如果种群在遗传上彼此不同,但没有通过距离效应显示出隔离,则可能是由于偶然的长距离定居,而由于建立者效应而发生了遗传差异。本研究的目的是在两个相反的景观结构中识别斑节对虾的种群结构:Do?ana国家公园的相当连续的栖息地,以及芬兰南部森林砍伐和岛屿的自然零星分布。

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