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Measuring the effects of forest extent and road traffic on anuran populations.

机译:衡量森林范围和道路交通对无ur种群的影响。

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Landscape ecologists have made large strides in the last 15 years in understanding the effect that landscape structure has on the abundance and persistence of organisms. However, conducting research at the landscape scale brings with it a number of methodological challenges. In this thesis, I use careful site selection and novel analytical techniques to examine the effects of forest extent and road traffic on anuran populations, and, more generally, examine how methodological issues affect landscape-scale inference. I address four questions: (1) What is the effect of experimental design on landscape-scale inference? (2) What are the relative effects of road traffic and forest extent on anuran populations? (3) What are the combined effects of a major highway and the forest extent near it on anuran populations? (4) What is the road effect zone of a major intercity highway for anurans?;I showed that sub-optimal study design at the landscape scale -- particularly incomplete sampling across the possible range of values in a predictor variable and correlations between landscape-scale predictors - is likely to have a major impact on landscape-scale inference. I then showed that the negative effect of road traffic is three times as great as the landscape-scale effect of deforestation on anuran species richness in eastern Ontario when these two predictor variables are considered independently. Having established that road traffic has an important negative effect on anurans, I then focused on better understanding how roads affect wildlife. First, I showed that a novel measure of the combined effects of roads and habitat loss on wildlife - accessible habitat - was a better predictor of anuran species richness near a major highway (Highway 401) than considering distance to the highway and habitat amount alone. I then showed that the negative effect of Highway 401 on anuran populations extends at least 500 m into the landscape. Overall, my results suggest that sub-optimal study design has likely led to an underestimate of the true effect of roads on wildlife. More generally, careful study design is necessary for landscape-scale studies to continue to provide meaningful guidelines for conservation.
机译:在过去的15年中,景观生态学家在了解景观结构对生物的丰度和持久性的影响方面取得了长足的进步。然而,在景观尺度上进行研究带来了许多方法上的挑战。在这篇论文中,我使用精心的选址和新颖的分析技术来考察森林范围和道路交通对无ur种群的影响,并且更广泛地讲,研究方法论问题如何影响景观尺度推断。我要解决四个问题:(1)实验设计对景观尺度推断的影响是什么? (2)道路交通和森林面积对无an种群的相对影响是什么? (3)一条主要公路及其附近的森林范围对无an种群的综合影响是什么? (4)大型无环城际公路对无金无环公路的道路影响区域是什么?;我证明了景观尺度上的次优研究设计-特别是在预测变量的可能值范围内的不完全采样以及景观之间的相关性-尺度预测器-可能会对景观尺度推断产生重大影响。然后,我表明,当独立考虑这两个预测变量时,道路交通的负面影响是安大略省东部地区森林砍伐对无草物种丰富度的景观尺度影响的三倍。在确定道路交通对无尾藻有重要的负面影响之后,我着重于更好地了解道路如何影响野生动植物。首先,我表明,与仅考虑与公路的距离和栖息地数量相比,一种衡量道路和栖息地丧失对野生生物的综合影响的新方法(可到达的栖息地)可以更好地预测主要公路(401高速公路)附近的无色动物物种丰富度。然后,我证明了401号高速公路对无芒种群的负面影响至少延伸了500 m到景观中。总体而言,我的结果表明,次优研究设计可能导致低估了道路对野生动植物的真实影响。一般而言,景观设计研究必须进行仔细的研究设计,才能继续为保护工作提供有意义的指导。

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