Ony Meher A, Nowicki Marcin, Boggess Sarah L, Klingeman William E, Zobel John M, Trigiano Robert N, Hadziabdic Denita
Department of Entomology and Plant Pathology University of Tennessee Knoxville TN USA.
Department of Plant Sciences University of Tennessee Knoxville TN USA.
Ecol Evol. 2020 Mar 16;10(8):3655-3670. doi: 10.1002/ece3.6141. eCollection 2020 Apr.
Forest fragmentation may negatively affect plants through reduced genetic diversity and increased population structure due to habitat isolation, decreased population size, and disturbance of pollen-seed dispersal mechanisms. However, in the case of tree species, effective pollen-seed dispersal, mating system, and ecological dynamics may help the species overcome the negative effect of forest fragmentation. A fine-scale population genetics study can shed light on the postfragmentation genetic diversity and structure of a species. Here, we present the genetic diversity and population structure of L. (eastern redbud) wild populations on a fine scale within fragmented areas centered around the borders of Georgia-Tennessee, USA. We hypothesized high genetic diversity among the collections of distributed across smaller geographical ranges. Fifteen microsatellite loci were used to genotype 172 individuals from 18 unmanaged and naturally occurring collection sites. Our results indicated presence of population structure, overall high genetic diversity ( = 0.63, = 0.34), and moderate genetic differentiation ( = 0.14) among the collection sites. Two major genetic clusters within the smaller geographical distribution were revealed by STRUCTURE. Our data suggest that native populations in the fragmented area around the Georgia-Tennessee border were able to maintain high levels of genetic diversity, despite the presence of considerable spatial genetic structure. As habitat isolation may negatively affect gene flow of outcrossing species across time, consequences of habitat fragmentation should be regularly monitored for this and other forest species. This study also has important implications for habitat management efforts and future breeding programs.
森林破碎化可能会对植物产生负面影响,这是由于栖息地隔离、种群规模减小以及花粉 - 种子传播机制受到干扰,导致遗传多样性降低和种群结构增加。然而,对于树种而言,有效的花粉 - 种子传播、交配系统和生态动态可能有助于物种克服森林破碎化的负面影响。一项精细尺度的种群遗传学研究可以揭示一个物种在破碎化后的遗传多样性和结构。在这里,我们展示了在美国佐治亚州 - 田纳西州边界周围的破碎区域内,小叶紫荆(东部紫荆)野生种群在精细尺度上的遗传多样性和种群结构。我们假设分布在较小地理范围内的小叶紫荆种群间具有较高的遗传多样性。使用15个微卫星位点对来自18个未管理的自然发生采集地点的172个个体进行基因分型。我们的结果表明,采集地点之间存在种群结构、总体遗传多样性较高(H O = 0.63,H E = 0.34)以及中等程度的遗传分化(F ST = 0.14)。STRUCTURE分析揭示了在较小地理分布范围内的两个主要遗传簇。我们的数据表明,尽管存在相当大的空间遗传结构,但佐治亚州 - 田纳西州边界周围破碎区域内的小叶紫荆原生种群能够保持较高水平的遗传多样性。由于栖息地隔离可能会随着时间的推移对异交物种的基因流动产生负面影响,因此应该定期监测栖息地破碎化对该物种和其他森林物种的影响。这项研究对栖息地管理工作和未来的育种计划也具有重要意义。