National Oceanic and Atmospheric Administration (NOAA) Fisheries, Northwest Fisheries Science Center, 2725 Montlake Boulevard East, Seattle, Washington 98112, USA.
Integr Environ Assess Manag. 2011 Oct;7(4):648-56. doi: 10.1002/ieam.219. Epub 2011 Jul 22.
Since the late 1990 s, monitoring efforts evaluating the effectiveness of urban stream restoration projects in the greater metropolitan area of Seattle, Washington, USA, have detected high rates of premature mortality among adult coho salmon (Oncorhynchus kisutch) in restored spawning habitats. Affected animals display a consistent suite of symptoms (e.g., disorientation, lethargy, loss of equilibrium, gaping, fin splaying) that ultimately progresses to death on a timescale of a few hours. Annual rates of prespawn mortality observed over multiple years, across several drainages, have ranged from approximately 20% to 90% of the total fall run within a given watershed. Current weight-of-evidence suggests that coho prespawn mortality is caused by toxic urban stormwater runoff. To evaluate the potential consequences of current and future urbanization on wild coho salmon, we constructed life-history models to estimate the impacts of prespawn mortality on coho populations and metapopulations. At the low (20%) and high (90%) ends of the range of observed mortality, model results indicated the mean time to extinction of localized coho populations in 115 and 8 y, respectively. The presence of productive source populations (i.e., unaffected by prespawn mortality) within a metapopulation reduced local extinction risk. However, as more populations within a metapopulation become affected by spawner die-offs prior to spawning, the source population's productivity declined. These simple models demonstrate the potential for rapid losses from coho populations in urbanizing watersheds. Because the models do not account for possible impacts of toxic runoff to other coho life stages, they likely underestimate the cumulative impacts of nonpoint source pollution on wild populations.
自 20 世纪 90 年代末以来,美国华盛顿州西雅图大都市区的城市溪流恢复项目的监测工作已经发现,在恢复的产卵栖息地中,成年银鲑(Oncorhynchus kisutch)的死亡率很高。受影响的动物表现出一致的症状(例如,迷失方向、昏睡、失去平衡、张口、鳍张开),最终在数小时内死亡。在多个流域多年观察到的产卵前死亡率,每年的死亡率范围约为总秋季洄游量的 20%至 90%。目前的证据表明,银鲑的产卵前死亡率是由有毒的城市雨水径流引起的。为了评估当前和未来城市化对野生银鲑的潜在影响,我们构建了生命史模型来估计产卵前死亡率对银鲑种群和集合种群的影响。在观察到的死亡率范围的低(20%)和高(90%)端,模型结果表明,局部银鲑种群灭绝的平均时间分别为 115 年和 8 年。集合种群中存在生产力较高的原始种群(即不受产卵前死亡率影响)降低了局部灭绝的风险。然而,随着集合种群中更多的种群在产卵前受到产卵死亡的影响,原始种群的生产力下降。这些简单的模型表明,城市化流域中银鲑种群可能迅速减少。由于模型没有考虑到有毒径流对其他银鲑生命阶段的可能影响,因此它们可能低估了非点源污染对野生种群的累积影响。