University College Dublin, School of Biology and Environmental Science, Science Centre West, Dublin 4, Ireland.
J Hered. 2012 Sep-Oct;103(5):661-71. doi: 10.1093/jhered/ess042. Epub 2012 Sep 4.
Human-mediated introduction of nonnative species into coastal areas via aquaculture is one of the main pathways that can lead to biological invasions. To develop strategies to counteract invasions, it is critical to determine whether populations establishing in the wild are self-sustaining or based on repeated introductions. Invasions by the Pacific oyster (Crassostrea gigas) have been associated with the growing oyster aquaculture industry worldwide. In this study, temporal genetic variability of farmed and wild oysters from the largest enclosed bay in Ireland was assessed to reconstruct the recent biological history of the feral populations using 7 anonymous microsatellites and 7 microsatellites linked to expressed sequence tags (ESTs). There was no evidence of EST-linked markers showing footprints of selection. Allelic richness was higher in feral than in aquaculture samples (P = 0.003, paired t-test). Significant deviations from Hardy-Weinberg equilibrium due to heterozygote deficiencies were detected for almost all loci and samples, most likely explained by the presence of null alleles. Relatively high genetic differentiation was found between aquaculture and feral oysters (largest pairwise multilocus F(ST) 0.074, P < 0.01) and between year classes of oysters from aquaculture (largest pairwise multilocus F(ST) 0.073, P < 0.01), which was also confirmed by the strong separation of aquaculture and wild samples using Bayesian clustering approaches. A 10-fold higher effective population size (N(e)) and a high number of private alleles in wild oysters suggest an established self-sustaining feral population. The wild oyster population studied appears demographically independent from the current aquaculture activities in the estuary and alternative scenarios of introduction pathways are discussed.
人类通过水产养殖将非本地物种引入沿海地区是导致生物入侵的主要途径之一。为了制定对抗入侵的策略,确定在野外建立的种群是自我维持的还是基于反复引入的,这一点至关重要。太平洋牡蛎(Crassostrea gigas)的入侵与全球不断发展的牡蛎水产养殖业有关。在这项研究中,评估了爱尔兰最大封闭湾中养殖和野生牡蛎的时间遗传变异性,使用 7 个匿名微卫星和 7 个与表达序列标签(EST)相关的微卫星来重建野生种群的近期生物学历史。没有证据表明 EST 相关标记显示出选择的痕迹。野生样本的等位基因丰富度高于养殖样本(P = 0.003,配对 t 检验)。由于杂合子缺乏,几乎所有位点和样本都检测到偏离 Hardy-Weinberg 平衡的显著偏差,最有可能是由无效等位基因的存在解释的。养殖和野生牡蛎之间(最大成对多基因座 F(ST) 0.074,P < 0.01)以及养殖牡蛎的年龄组之间(最大成对多基因座 F(ST) 0.073,P < 0.01)发现相对较高的遗传分化,这也通过贝叶斯聚类方法证实了养殖和野生样本的强烈分离。野生牡蛎的有效种群大小(N(e))高 10 倍,并且存在大量的私有等位基因,这表明建立了一个自我维持的野生种群。研究中野生牡蛎种群在人口统计学上似乎与河口当前的水产养殖活动独立,并且讨论了其他引入途径的情景。