Geomatics and Landscape Ecology Research Laboratory (GLEL), Ottawa-Carleton Institute of Biology, Carleton University, 1125 Colonel By Drive, Ottawa, ON, K1S 5B6, Canada,
Oecologia. 2013 Nov;173(3):1143-56. doi: 10.1007/s00442-013-2684-x. Epub 2013 May 29.
In reviews on effects of roads on animal population abundance we found that most effects are negative; however, there are also many neutral and positive responses [Fahrig and Rytwinski (Ecol Soc 14:21, 2009; Rytwinski and Fahrig (Biol Conserv 147:87-98, 2012)]. Here we use an individual-based simulation model to: (1) confirm predictions from the existing literature of the combinations of species traits and behavioural responses to roads that lead to negative effects of roads on animal population abundance, and (2) improve prediction of the combinations of species traits and behavioural responses to roads that lead to neutral and positive effects of roads on animal population abundance. Simulations represented a typical situation in which road mitigation is contemplated, i.e. rural landscapes containing a relatively low density (up to 1.86 km/km(2)) of high-traffic roads, with continuous habitat between the roads. In these landscapes, the simulations predict that populations of species with small territories and movement ranges, and high reproductive rates, i.e. many small mammals and birds, should not be reduced by roads. Contrary to previous suggestions, the results also predict that populations of species that obtain a resource from roads (e.g. vultures) do not increase with increasing road density. In addition, our simulations support the predation release hypothesis for positive road effects on prey (both small- and large-bodied prey), whereby abundance of a prey species increased with increasing road density due to reduced predation by generalist road-affected predators. The simulations also predict an optimal road density for the large-bodied prey species if it avoids roads or traffic emissions. Overall, the simulation results suggest that in rural landscapes containing high-traffic roads, there are many species for which road mitigation may not be necessary; mitigation efforts should be tailored to the species that show negative population responses to roads.
在关于道路对动物种群数量影响的综述中,我们发现大多数影响是负面的;然而,也有许多中性和积极的反应[Fahrig 和 Rytwinski(Ecol Soc 14:21, 2009;Rytwinski 和 Fahrig(Biol Conserv 147:87-98, 2012)]。在这里,我们使用基于个体的模拟模型来:(1)确认现有文献中关于物种特征和对道路的行为反应的组合的预测,这些预测导致道路对动物种群数量的负面影响,以及(2)改进预测导致道路对动物种群数量产生中性和积极影响的物种特征和对道路的行为反应的组合。模拟代表了考虑道路缓解的典型情况,即在含有相对低密度(高达 1.86 km/km²)的高交通道路和道路之间连续栖息地的农村景观中。在这些景观中,模拟预测,具有小领地和运动范围以及高繁殖率的物种的种群,即许多小型哺乳动物和鸟类,不应被道路减少。与先前的建议相反,结果还预测,从道路获得资源的物种的种群(例如秃鹫)不会随着道路密度的增加而增加。此外,我们的模拟结果支持捕食者释放假说,即道路对猎物(大小型猎物)产生积极影响,由于受道路影响的一般捕食者捕食减少,猎物物种的丰度随着道路密度的增加而增加。模拟结果还预测了大型猎物物种的最佳道路密度,如果它避免道路或交通排放。总体而言,模拟结果表明,在含有高交通量道路的农村景观中,有许多物种不需要进行道路缓解;缓解工作应针对对道路产生负面种群反应的物种进行调整。