首页> 外文学位 >Direct and indirect effects of predation on genetic variability and phenotypic divergence in yellow perch (Perca flavescens).
【24h】

Direct and indirect effects of predation on genetic variability and phenotypic divergence in yellow perch (Perca flavescens).

机译:捕食对黄鲈(Perca flavescens)遗传变异和表型差异的直接和间接影响。

获取原文
获取原文并翻译 | 示例

摘要

Yellow perch (Perca flavescens) are relatively acid- and metal-tolerant and often persist as one of the few remaining fish species in a damaged/acidified lake or are at least one of the species that first colonizes a lake once water quality improves. However, with time and increased chemical recovery in Sudbury lakes, other fish species that are potential predators of perch (e.g., walleye (Sander vitreus), smallmouth bass (Micropterus dolomieu), northern pike ( Esox lucius)) are also beginning to colonize Sudbury lakes. As these lakes recover, perch are therefore forced to cope not only with persistent stressful chemical conditions but must also adapt to changes in predation and intra/interspecific competition for food resources. Such predation or competition pressures often lead to habitat polymorphisms that involve the exploitation of two very different habitats: the littoral (or nearshore) and the pelagic (open water) zones. The addition of a predator to an established perch population generally causes the perch to abandon the pelagic zone and increase their use of the littoral habitat.;Microsatellite genotyping is an efficient and powerful tool that can provide information about the genetic structure of populations. However, it is known to be prone to errors that can affect downstream analysis. Genotyping errors in my study caused several microsatellite loci to be dropped from the analysis, which decreased the statistical significance of my results. Despite this, there are interesting trends that were revealed and recommendations for further analysis to increase the robustness of the study are suggested.;Initial analysis revealed that differences in genetic variability between perch in littoral and pelagic habitats accounted for 2% of the total variability among lakes. This evidence suggests that the increase in littoral habitat use affects, or is associated with, changes in the genetic variability of the littoral population. There was also a positive correlation between perch biomass and genetic variability in both the littoral and pelagic habitat.;The results suggest that the type of predator and its preferred location may play a role in determining the dispersal of yellow perch and consequently their levels of genetic variability. In lakes where the primary predator was smallmouth bass, a littoral zone predator, the genetic variability of perch in the littoral zone was slightly higher than in the pelagic zone. On the other hand, in lakes where the primary predator is walleye, a pelagic predator, the pattern reversed and the genetic variability of perch in the pelagic habitat was slightly higher than in the littoral zone.;In this study, genetic structure was assessed over two years in Sudbury yellow perch populations within littoral and pelagic habitats along a predation gradient in eight lakes using microsatellite genotyping. One of the study lakes (Hannah Lake) was experimentally manipulated by adding predators (smallmouth bass) to a perch population, thus creating a unique opportunity to study the immediate effects of predators on the genetic structure and morphological traits of a perch population.;Habitat polymorphisms can also lead to changes in morphological traits such as those associated with adaptation to food resources or predator avoidance. Analysis of ten morphological characteristics was conducted to allow comparisons between genetic and phenotypic differentiation. Results from this study suggest that these morphological traits are under divergent selection and represent local adaptations.;These results provide support for the link between predation pressure, phenotypic plasticity, and genetic structure of perch population. The presence of predators appears to be associated with differences in genetic variability in yellow perch populations across habitat gradients. These genetic differences occur over small spatial scales and should be taken into consideration when planning conservation efforts. Genetic variation is hypothesized to be key for long-term evolutionary change and short-term environmental adaptation and, thus, has the potential to influence restoration efforts.
机译:黄鲈(Perca flavescens)相对耐酸和耐金属,通常作为受损/酸化的湖泊中剩余的少数鱼类之一而存在,或者至少是一旦水质改善而首先在湖泊中定殖的鱼类之一。然而,随着时间的推移以及萨德伯里湖中化学物质的恢复,其他可能栖息的鱼类(例如大眼鲷(沙嘴玻璃体),小嘴鲈鱼(小白鲈),北梭鱼(Esox lucius))也开始在萨德伯里定居。湖泊。随着这些湖泊的恢复,鲈鱼不仅被迫应对持续的紧张化学条件,而且还必须适应捕食的变化以及种内/种间对食物资源的竞争。这种掠夺或竞争压力常常导致栖息地多态性,涉及对两个非常不同的栖息地的开发:沿海(或近岸)和远洋(开放水域)带。在既定的栖息种群中增加捕食者通常会使栖息者放弃上层带并增加其对沿海栖息地的利用。微卫星基因分型是一种可以提供有关种群遗传结构信息的有效而强大的工具。但是,已知容易出现会影响下游分析的错误。我的研究中的基因分型错误导致从分析中删除了几个微卫星基因座,这降低了我的结果的统计学意义。尽管如此,还是发现了有趣的趋势,并提出了进一步分析的建议,以提高研究的可靠性。初始分析表明,沿海和中上生境栖息地之间鲈鱼的遗传变异性差异占总变异性的2%湖泊。该证据表明,沿岸栖息地使用的增加影响或与沿岸种群遗传变异的变化有关。滨海和中上层栖息地的鲈鱼生物量与遗传变异性之间也呈正相关。结果表明,捕食者的类型及其首选位置可能在决定黄鲈的扩散及其遗传水平方面起作用。变化性。在主要捕食者是小嘴鲈(沿海区捕食者)的湖泊中,沿海区鲈鱼的遗传变异性略高于中上层带。另一方面,在主要捕食者为角膜上皮捕食者的湖泊中,其模式反转并且中上层栖息地鲈鱼的遗传变异性略高于沿海地区。在萨德伯里,使用微卫星基因型分型在沿八个湖泊的捕食梯度沿岸和中上生境中栖息的黄鲈种群为期两年。通过对鲈鱼种群添加捕食者(小嘴鲈),对其中一个研究湖泊(汉娜湖)进行了实验性操作,从而为研究捕食者对鲈鱼种群的遗传结构和形态特征的直接影响提供了独特的机会。多态性还可以导致形态特征的变化,例如与适应粮食资源或避免捕食相关的特征。进行了十种形态特征的分析,以便比较遗传分化和表型分化。这项研究的结果表明,这些形态特征处于不同的选择之下,并代表了局部适应性。这些结果为捕食压力,表型可塑性和鲈鱼种群遗传结构之间的联系提供了支持。捕食者的存在似乎与跨栖息地梯度的黄鲈种群遗传变异的差异有关。这些遗传差异发生在较小的空间尺度上,在计划保护工作时应予以考虑。假设遗传变异是长期进化变化和短期环境适应的关键,因此有可能影响恢复工作。

著录项

  • 作者

    Tremblay, Ashley S.;

  • 作者单位

    Laurentian University (Canada).;

  • 授予单位 Laurentian University (Canada).;
  • 学科 Biology Genetics.;Biology Limnology.
  • 学位 M.Sc.
  • 年度 2009
  • 页码 67 p.
  • 总页数 67
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号