Meffe Gary K
University of Georgia's Savannah River Ecology Lab Aiken South Carolina USA.
Fisheries (Bethesda). 1986 Jan;11(1):14-23. doi: 10.1577/1548-8446(1986)011<0014:CGATMO>2.0.CO;2. Epub 2011 Jan 9.
The emerging field of endangered fishes management has yet to fully incorporate conservation genetics into recovery programs. Genetic aspects of small populations must be considered at the outset of management programs in order to maximize probability of their long-term survival and continued adaptability. Total genetic variance of a species consists of within population genetic diversity, and the differences found among populations; both types of variance should be maintained to maximize adaptive flexibility of endangered fishes. Forces that erode genetic variation include small population size, population bottlenecks, genetic drift, inbreeding depression, artificial selection in captivity, and mixing of distinct genetic stocks. These can lead to increased homozygosity, loss of quantitative variation, and exposure of deleterious recessive alleles, all of which may reduce fitness. Suggestions for genetically sound management of endangered fishes include genetic monitoring of natural and captive populations, use of large numbers for captive breeding where feasible, selective mating to avoid inbreeding where necessary, minimization of time in captivity, and separate maintenance of distinct stocks.
濒危鱼类管理这一新兴领域尚未将保护遗传学全面纳入恢复计划。在管理计划开始时就必须考虑小种群的遗传因素,以便最大限度地提高其长期生存和持续适应能力的可能性。一个物种的总遗传变异包括种群内的遗传多样性以及种群间的差异;这两种变异类型都应予以维持,以最大限度地提高濒危鱼类的适应性灵活性。侵蚀遗传变异的因素包括种群规模小、种群瓶颈、遗传漂变、近亲繁殖衰退、圈养中的人工选择以及不同遗传种群的混合。这些因素会导致纯合性增加、数量变异丧失以及有害隐性等位基因的暴露,所有这些都可能降低适应性。对濒危鱼类进行合理遗传管理的建议包括对自然种群和圈养种群进行遗传监测,在可行的情况下使用大量个体进行圈养繁殖,必要时进行选择性交配以避免近亲繁殖,尽量缩短圈养时间,以及对不同种群进行分开饲养。