Jackson J A, Patenaude N J, Carroll E L, Baker C Scott
School of Biological Sciences, University of Auckland, Private Bag 92019, Auckland, New Zealand.
Mol Ecol. 2008 Jan;17(1):236-51. doi: 10.1111/j.1365-294X.2007.03497.x. Epub 2007 Sep 24.
Reconstructing the history of exploited populations of whales requires fitting a trajectory through at least three points in time: (i) prior to exploitation, when abundance is assumed to be at the maximum allowed by environmental carrying capacity; (ii) the point of minimum abundance or 'bottleneck', usually near the time of protection or the abandonment of the hunt; and (iii) near the present, when protected populations are assumed to have undergone some recovery. As historical abundance is usually unknown, this trajectory must be extrapolated according to a population dynamic model using catch records, an assumed rate of increase and an estimate of current abundance, all of which have received considerable attention by the International Whaling Commission (IWC). Relatively little attention has been given to estimating minimum abundance (N(min)), although it is clear that genetic and demographic forces at this point are critical to the potential for recovery or extinction of a local population. We present a general analytical framework to improve estimates of N(min) using the number of mtDNA haplotypes (maternal lineages) surviving in a contemporary population of whales or other exploited species. We demonstrate the informative potential of this parameter as an a posteriori constraint on Bayesian logistic population dynamic models based on the IWC Comprehensive Assessment of the intensively exploited southern right whales (Eubalaena australis) and published surveys of mtDNA diversity for this species. Estimated historical trajectories from all demographic scenarios suggested a substantial loss of mtDNA haplotype richness as a result of 19th century commercial whaling and 20th century illegal whaling by the Soviet Union. However, the relatively high rates of population increase used by the IWC assessment predicted a bottleneck that was implausibly narrow (median, 67 mature females), given our corrected estimates of N(min). Further, high levels of remnant sequence diversity (theta) suggested that pre-exploitation abundance was larger than predicted by the logistic model given the catch record, which is known to be incomplete. Our results point to a need to better integrate evolutionary processes into population dynamic models to account for uncertainty in catch records, the influence of maternal fidelity on metapopulation dynamics, and the potential for inverse density dependence (an 'Allee effect') in severely depleted populations.
重建被捕鲸种群的历史,需要拟合出至少三个时间点的种群变化轨迹:(i)捕鲸活动开始之前,此时假定种群数量处于环境承载能力所允许的最大值;(ii)种群数量最低点或“瓶颈期”,通常接近保护措施实施之时或捕鲸活动停止之时;(iii)接近当前时间,此时假定受保护种群已经有所恢复。由于历史上的种群数量通常未知,因此必须根据种群动态模型,利用捕鲸记录、假定的增长率以及当前种群数量估计值来推断这一轨迹,国际捕鲸委员会(IWC)对所有这些方面都给予了相当多的关注。尽管很明显,此时的遗传和人口统计学因素对于当地种群的恢复或灭绝潜力至关重要,但对最低种群数量(N(min))的估计却相对较少受到关注。我们提出了一个通用的分析框架,利用当代鲸鱼或其他被捕捞物种种群中存活的线粒体DNA单倍型(母系谱系)数量来改进对N(min)的估计。基于国际捕鲸委员会对密集捕捞的南露脊鲸(Eubalaena australis)的综合评估以及已发表的该物种线粒体DNA多样性调查,我们证明了这一参数作为贝叶斯逻辑斯谛种群动态模型的后验约束的信息潜力。所有人口统计学情景下估计的历史轨迹表明,由于19世纪的商业捕鲸以及20世纪苏联的非法捕鲸,线粒体DNA单倍型丰富度大幅下降。然而,根据我们对N(min)的校正估计,国际捕鲸委员会评估中使用的相对较高的种群增长率预测出的瓶颈期窄得难以置信(中位数为67头成年雌性)。此外,高水平的残余序列多样性(theta)表明,考虑到已知不完整的捕鲸记录,捕鲸前的种群数量比逻辑斯谛模型预测的要大。我们的结果表明,有必要将进化过程更好地整合到种群动态模型中,以考虑捕鲸记录中的不确定性、母系保真度对集合种群动态的影响,以及严重枯竭种群中逆密度依赖性(“阿利效应”)的可能性。