Alter S Elizabeth, Ramirez Sergio Flores, Nigenda Sergio, Ramirez Jorge Urbán, Bracho Lorenzo Rojas, Palumbi Stephen R
Department of Biological Sciences, Hopkins Marine Station, Stanford University, 120 Oceanview Boulevard, Pacific Grove, CA 93950, USA.
J Hered. 2009 Jan-Feb;100(1):34-46. doi: 10.1093/jhered/esn090. Epub 2008 Oct 30.
Accurate knowledge of population structure in cetaceans is critical for preserving and managing breeding habitat, particularly when habitat is not uniformly protected. Most eastern gray whales return to their major breeding range each winter along the Pacific coast of Baja California, Mexico, concentrating in 3 major calving lagoons, but it is unknown whether genetic differences exist between lagoons. Previous photo-identification studies and genetic studies suggest that gray whales may return to their natal lagoons to breed, potentially resulting in the buildup of genetic differences. However, an earlier genetic study used only one genetic marker and did not include samples from Bahia Magdalena, a major calving lagoon not currently designated as a wildlife refuge. To expand on this previous study, we collected genetic data from the mitochondrial control region (442 bp) and 9 microsatellite markers from 112 individuals across all 3 major calving lagoons. Our data suggest that migration rates between calving lagoons are high but that a small but significant departure from panmixia exists between Bahia Magdalena and Laguna San Ignacio (Fisher's Exact test, P < 0.0001; F(ST) = 0.006, P = 0.025). Coalescent simulations show that the lack of extensive population structure may result from the disruption of structure due to whaling. Another possibility is that rates of migration have always been high (>10% per generation). In addition, microsatellite data showed evidence of a severe population bottleneck. Eastern gray whales are still recovering from the impacts of whaling on their breeding grounds, and these populations should be protected and monitored for future genetic changes.
准确了解鲸类动物的种群结构对于保护和管理繁殖栖息地至关重要,尤其是当栖息地没有得到统一保护时。大多数东部灰鲸每年冬天都会返回墨西哥下加利福尼亚州太平洋沿岸的主要繁殖区域,集中在3个主要的产犊泻湖,但尚不清楚这些泻湖之间是否存在遗传差异。先前的照片识别研究和基因研究表明,灰鲸可能会返回其出生的泻湖进行繁殖,这可能会导致遗传差异的积累。然而,一项早期的基因研究仅使用了一个基因标记,并且没有包括来自马格达莱纳湾(一个目前未被指定为野生动物保护区的主要产犊泻湖)的样本。为了扩展先前的这项研究,我们从所有3个主要产犊泻湖的112个个体中收集了线粒体控制区(442 bp)的基因数据和9个微卫星标记。我们的数据表明,产犊泻湖之间的迁移率很高,但马格达莱纳湾和圣伊格纳西奥泻湖之间存在轻微但显著的偏离随机交配现象(费舍尔精确检验,P < 0.0001;F(ST) = 0.006,P = 0.025)。溯祖模拟表明,缺乏广泛的种群结构可能是由于捕鲸导致的结构破坏。另一种可能性是迁移率一直很高(每代>10%)。此外,微卫星数据显示出严重种群瓶颈的证据。东部灰鲸仍在从捕鲸对其繁殖地的影响中恢复,这些种群应受到保护并监测未来的基因变化。