Biological Sciences, University of Arkansas, Fayetteville, Arkansas, United States of America.
Southwestern Native Aquatic Resources and Recovery Center, U.S. Fish & Wildlife Service, Dexter, New Mexico, United States of America.
PLoS One. 2021 Dec 9;16(12):e0260344. doi: 10.1371/journal.pone.0260344. eCollection 2021.
Ecological restoration can promote biodiversity conservation in anthropogenically fragmented habitats, but effectiveness of these management efforts need to be statistically validated to determine 'success.' One such approach is to gauge the extent of recolonization as a measure of landscape permeability and, in turn, population connectivity. In this context, we estimated dispersal and population connectivity in prairie vole (Microtus ochrogaster; N = 231) and meadow vole (M. pennsylvanicus; N = 83) within five tall-grass prairie restoration sites embedded within the agricultural matrix of midwestern North America. We predicted that vole dispersal would be constrained by the extent of agricultural land surrounding restored habitat patches, spatially isolating vole populations and resulting in significant genetic structure. We first employed genetic assignment tests based on 15 microsatellite DNA loci to validate field-derived species-designations, then tested reclassified samples with multivariate and Bayesian clustering to assay for spatial and temporal genetic structure. Population connectivity was further evaluated by calculating pairwise FST, then potential demographic effects explored by computing migration rates, effective population size (Ne), and average relatedness (r). Genetic species assignments reclassified 25% of initial field identifications (N = 11 M. ochrogaster; N = 67 M. pennsylvanicus). In M. ochrogaster population connectivity was high across the study area, reflected in little to no spatial or temporal genetic structure. In M. pennsylvanicus genetic structure was detected, but relatedness estimates identified it as kin-clustering instead, underscoring social behavior among populations rather than spatial isolation as the cause. Estimates of Ne and r were stable across years, reflecting high dispersal and demographic resilience. Combined, these metrics suggest the agricultural matrix is highly permeable for voles and does not impede dispersal. High connectivity observed confirms that the restored landscape is productive and permeable for specific management targets such as voles and also demonstrates population genetic assays as a tool to statistically evaluate effectiveness of conservation initiatives.
生态恢复可以促进人为破碎生境中的生物多样性保护,但这些管理工作的效果需要通过统计学验证来确定“成功”。一种方法是衡量再定殖程度,作为衡量景观渗透性的指标,并进而衡量种群连通性。在这种情况下,我们估计了草原田鼠(Microtus ochrogaster;N=231)和草地田鼠(M. pennsylvanicus;N=83)在北美中西部农业基质内的五个高草草原恢复点内的扩散和种群连通性。我们预测,田鼠的扩散将受到周围农业用地的限制,从而隔离田鼠种群,并导致显著的遗传结构。我们首先采用基于 15 个微卫星 DNA 座的遗传分配测试来验证现场得出的物种分类,然后使用多元和贝叶斯聚类来测试重新分类的样本,以确定空间和时间遗传结构。通过计算成对 FST 进一步评估了种群连通性,然后通过计算迁移率、有效种群大小(Ne)和平均亲缘关系(r)来探索潜在的人口动态效应。遗传物种分配重新分类了 25%的初始现场鉴定(N=11 M. ochrogaster;N=67 M. pennsylvanicus)。在 M. ochrogaster 种群中,整个研究区域的连通性很高,反映出很少有空间或时间遗传结构。在 M. pennsylvanicus 中检测到遗传结构,但亲缘关系估计表明这是亲缘聚类,而不是空间隔离,这突出了种群之间的社会行为,而不是空间隔离是造成这种情况的原因。Ne 和 r 的估计在各年均保持稳定,反映了高扩散和人口恢复力。综上所述,这些指标表明农业基质对田鼠具有高度渗透性,不会阻碍扩散。观察到的高连通性证实,恢复后的景观对于特定的管理目标(如田鼠)是富有成效和可渗透的,也证明了种群遗传检测是一种统计评估保护计划效果的工具。