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Butterfly conservation in fragmented landscapes.

机译:零散景观中的蝴蝶保护。

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摘要

Human activities disturb and fragment many natural areas, thereby altering the way in which species interact with their landscape. In natural settings, species often evolved to disperse through areas unsuitable for habitation, but in a world dominated by human-modified landscapes, species face novel features that may disrupt their movement, increasing the isolation of populations. Consequently, there is a pressing need to understand if animals can persist in small natural areas separated by agricultural or urban development. The way in which species respond to fragmentation will inform if conservation actions are necessary to protect a species and what strategies might mitigate the consequences of fragmentation. My dissertation addresses these conservation problems using two studies of butterflies in fragmented landscapes.;First, I used a novel synthesis of behavioral, mark-recapture, and population genetic studies to identify the effects of urban fragmentation on a rare butterfly. I present the synthesis in the context of a butterfly endemic to barrier islands in North Carolina, Atrytonopsis new species 1. Atrytonopsis sp1 occupies sand dune habitat, which in this region has largely been converted to residential and commercial development. Many studies rely on a single method to measure movement, but combining methods may help elucidate the effects of natural or anthropogenic fragmentation. To test edge permeability, I conducted butterfly releases at four edge types: sand dune - beach, sand dune - maritime forest/shrub, sand dune - urbanization, and beach - ocean. I then used mark-recapture to compare Atrytonopsis sp1 movement rates in continuous sand dune habitat and between habitat patches separated by urban areas. Finally, I conducted a range-wide population genetic study to assess if there was significant population structure across the range of Atrytonopsis sp1, and to determine how the structure was partitioned relative to natural barriers and urbanization. All three studies independently indicate that natural features, not urbanization, are barriers to Atrytonopsis sp1 movement. Analyzed separately, each study would point to the same general conclusion, but could result in different conservation recommendations. Both linear corridors and stepping-stones are conservation strategies that can increase connectivity of fragmented landscapes. For stepping stones to work, however, Atrytonopsis sp1 must be willing to enter the matrix, successfully find new habitat, and integrate its genes into the new population. The edge behavior studies indicate that Atrytonopsis sp1 will fly into urban areas, and the mark-recapture studies confirm that it can successfully disperse over short distances. The population genetic studies indicate that longer distances of urbanization are not intrinsically barriers to movement. Consequently, I recommend conservation strategies that focus on preserving stepping stones, rather than on habitat corridors.;In a separate study, I examined the effects of habitat fragmentation on tropical butterfly communities. Habitat fragmentation is a major driver of biodiversity loss, but its effects may be obscured by the ways in which different species respond to fragmentation. One reason that species display varying responses to fragmentation may be that variability itself is an effect of fragmentation. I tested whether forest fragmentation causes long-term hyperdynamism in butterfly communities, a taxon that naturally displays large variations in species richness and community composition. Using an 11-year dataset from an experimentally fragmented landscape in the central Amazon, I evaluated the effect of fragmentation on changes in species richness and community composition through time. Butterfly species richness did not differ between fragmented forest and intact forest. However, spatial and temporal patterns of butterfly species richness in fragmented forests were significantly more variable than in intact forest. Fragmented forest had a significantly lower proportion of understory shade species and a significantly higher proportion of edge species. I conclude that fragmentation fundamentally alters the natural dynamics of butterfly communities.
机译:人类活动扰乱和破坏了许多自然区域,从而改变了物种与其景观相互作用的方式。在自然环境中,物种通常进化为散布到不适合居住的区域,但是在一个以人为改变的景观为主导的世界中,物种面临的新特征可能会扰乱其活动,从而加剧了种群的隔离。因此,迫切需要了解动物是否可以在由农业或城市发展所分隔的较小自然区域中生存。物种对碎片的反应方式将告知是否有必要采取保护措施来保护物种,以及采取哪些策略来减轻碎片的后果。本文通过对蝴蝶在零散景观中的两个研究来解决这些保护问题。首先,我使用行为,标记夺回和种群遗传学研究的新颖合成方法来鉴定城市碎片对一只稀有蝴蝶的影响。我介绍了在北卡罗来纳州的屏障岛特有的蝴蝶,属Atrytonopsis新物种1的背景下进行的合成。Atrytonopsis sp1占据了沙丘生境,在该地区已被大部分转变为住宅和商业开发。许多研究都依靠一种方法来测量运动,但结合使用这些方法可能有助于阐明自然或人为破碎的影响。为了测试边缘渗透性,我对四种边缘类型进行了蝴蝶释放:沙丘-海滩,沙丘-海洋森林/灌木,沙丘-城市化和海滩-海洋。然后,我使用标记重获来比较连续沙丘生境中以及市区分隔的生境斑块之间的Atrytonopsis sp1运动速率。最后,我进行了一项范围广泛的种群遗传研究,以评估在Atrytonopsis sp1的整个范围内是否存在显着的种群结构,并确定相对于自然屏障和城市化如何划分结构。所有这三项研究独立地表明,自然特征而非城市化是Atrytonopsis sp1运动的障碍。分别进行分析,每项研究将指向相同的一般结论,但可能会提出不同的保护建议。线性走廊和垫脚石都是可以提高零散景观的连通性的保护策略。但是,要使踏脚石起作用,Atrytonopsis sp1必须愿意进入矩阵,成功找到新的栖息地,并将其基因整合到新的种群中。边缘行为研究表明Atrytonopsis sp1会飞入市区,并且标记捕获研究证实它可以在短距离内成功分散。人口遗传学研究表明,更长的城市化距离本质上不是移动的障碍。因此,我建议采用的保护策略应侧重于保护垫脚石,而不是栖息地走廊。在另一项研究中,我研究了栖息地破碎化对热带蝴蝶群落的影响。生境破碎化是生物多样性丧失的主要驱动力,但其影响可能因不同物种对破碎化反应的方式而被掩盖。物种显示出对碎片反应不同的一个原因可能是变异性本身就是碎片的影响。我测试了森林破碎是否会在蝴蝶群落中引起长期的过度活力,蝴蝶群落是自然显示物种丰富度和群落组成差异很大的分类单元。我使用来自亚马逊中部一个实验性破碎化景观的11年数据集,评估了破碎化对物种丰富度和群落组成随时间变化的影响。零散森林和完整森林之间的蝴蝶物种丰富度没有差异。但是,零碎森林中蝴蝶物种丰富度的时空格局比完整森林中的蝴蝶物种丰富度的变化更大。零散的森林的林下树荫物种比例明显较低,而边缘树种比例较高。我得出的结论是,碎片化从根本上改变了蝴蝶群落的自然动力。

著录项

  • 作者

    Leidner, Allison Kara.;

  • 作者单位

    North Carolina State University.;

  • 授予单位 North Carolina State University.;
  • 学科 Biology Ecology.;Biology Entomology.
  • 学位 Ph.D.
  • 年度 2009
  • 页码 128 p.
  • 总页数 128
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 生态学(生物生态学);昆虫学;
  • 关键词

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