Perera Omaththage P, Fescemyer Howard W, Fleischer Shelby J, Abel Craig A
Southern Insect Management Research Unit, USDA-ARS, Stoneville, MS 38776, USA.
Department of Biology, The Pennsylvania State University, University Park, PA 16802, USA.
Insects. 2020 Jul 23;11(8):463. doi: 10.3390/insects11080463.
Migrant populations of (Boddie) captured during 2002, 2005, 2016, and 2018 from Landisville and Rock Springs in Pennsylvania, USA were genotyped using 85 single nucleotide polymorphism (SNP) markers. Samples (n = 702) genotyped were divided into 16 putative populations based on collection time and site. Fixation indices (-statistics), analysis of molecular variance, and discriminant analysis of principal components were used to examine within and among population genetic variation. The observed and expected heterozygosity in putative populations ranged from 0.317-0.418 and 0.320-0.359, respectively. Broad range of (0.0-0.2742) and (0.0-0.2330) values indicated different genotype frequencies between and within the populations, respectively. High genetic diversity within and low genetic differentiation between populations was found in 2002 and 2005. Interestingly, high genetic differentiation between populations from two collection sites observed in 2018 populations was not evident in within-site comparisons of putative populations collected on different dates during the season. The shift of population genetic makeup in 2018 may be influenced by multiple biotic and abiotic factors including tropical storms. Continued assessment of these peripheral populations of will be needed to assess the impacts of genetic changes on pest control and resistance management tactics.
2002年、2005年、2016年和2018年期间,在美国宾夕法尼亚州兰迪斯维尔和岩泉捕获的(博迪)迁徙种群,使用85个单核苷酸多态性(SNP)标记进行基因分型。根据采集时间和地点,将基因分型的样本(n = 702)分为16个假定种群。使用固定指数(-统计量)、分子方差分析和主成分判别分析来检验种群内和种群间的遗传变异。假定种群中观察到的杂合度和预期杂合度分别为0.317 - 0.418和0.320 - 0.359。广泛的(0.0 - 0.2742)和(0.0 - 0.2330)值分别表明种群间和种群内不同的基因型频率。在2002年和2005年发现种群内遗传多样性高,种群间遗传分化低。有趣的是,2018年种群中观察到的来自两个采集地点的种群间高遗传分化,在该季节不同日期采集的假定种群的地点内比较中并不明显。2018年种群遗传组成的变化可能受到包括热带风暴在内的多种生物和非生物因素的影响。需要持续评估这些种群的边缘种群,以评估遗传变化对害虫控制和抗性管理策略的影响。