Kvalnes Thomas, Flagstad Øystein, Våge Jørn, Strand Olav, Viljugrein Hildegunn, Sæther Bernt-Erik
Norwegian Institute for Nature Research (NINA) Trondheim Norway.
Centre for Biodiversity Dynamics (CBD), Department of Biology Norwegian University of Science and Technology (NTNU) Trondheim Norway.
Evol Appl. 2024 Apr 11;17(4):e13684. doi: 10.1111/eva.13684. eCollection 2024 Apr.
Harvesting and culling are methods used to monitor and manage wildlife diseases. An important consequence of these practices is a change in the genetic dynamics of affected populations that may threaten their long-term viability. The effective population size ( ) is a fundamental parameter for describing such changes as it determines the amount of genetic drift in a population. Here, we estimate of a harvested wild reindeer population in Norway. Then we use simulations to investigate the genetic consequences of management efforts for handling a recent spread of chronic wasting disease, including increased adult male harvest and population decimation. The / ratio in this population was found to be 0.124 at the end of the study period, compared to 0.239 in the preceding 14 years period. The difference was caused by increased harvest rates with a high proportion of adult males (older than 2.5 years) being shot (15.2% in 2005-2018 and 44.8% in 2021). Increased harvest rates decreased in the simulations, but less sex biased harvest strategies had a lower negative impact. For harvest strategies that yield stable population dynamics, shifting the harvest from calves to adult males and females increased . Population decimation always resulted in decreased genetic variation in the population, with higher loss of heterozygosity and rare alleles with more severe decimation or longer periods of low population size. A very high proportion of males in the harvest had the most severe consequences for the loss of genetic variation. This study clearly shows how the effects of harvest strategies and changes in population size interact to determine the genetic drift of a managed population. The long-term genetic viability of wildlife populations subject to a disease will also depend on population impacts of the disease and how these interact with management actions.
捕猎和淘汰是用于监测和管理野生动物疾病的方法。这些做法的一个重要后果是受影响种群的遗传动态发生变化,这可能威胁到它们的长期生存能力。有效种群大小( )是描述此类变化的一个基本参数,因为它决定了种群中的遗传漂变程度。在此,我们估算了挪威一个被捕猎的野生驯鹿种群的有效种群大小。然后,我们使用模拟来研究应对近期慢性消耗病传播的管理措施的遗传后果,包括增加成年雄性的捕猎量和种群数量减少。研究期末该种群的 / 比率为0.124,而在前一个14年期间为0.239。这种差异是由于捕猎率增加,其中高比例的成年雄性(2.5岁以上)被射杀(2005 - 2018年为15.2%,2021年为44.8%)。在模拟中,增加的捕猎率降低了有效种群大小,但性别偏向性较小的捕猎策略负面影响较小。对于能产生稳定种群动态的捕猎策略,将捕猎对象从小牛转移到成年雄性和雌性会增加有效种群大小。种群数量减少总是导致种群遗传变异减少,杂合性和稀有等位基因的损失更大,种群数量减少越严重或低种群数量持续时间越长,损失就越大。捕猎中极高比例的雄性对遗传变异的损失影响最为严重。这项研究清楚地表明了捕猎策略的影响和种群大小的变化如何相互作用来决定受管理种群的遗传漂变。受疾病影响野生动物种群的长期遗传生存能力还将取决于疾病对种群的影响以及这些影响如何与管理行动相互作用。