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Precision of Population Viability Analysis - ResearchGate

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Ellner et al. <strong>Precision</strong> <strong>of</strong> PVA 259simulations. White (2000) and Sæther et al. (2000) showhow to use simulations to obtain confidence intervals forcomplicated models. Alternatively, confidence intervalscan be obtained for some models by repeatedly resamplingreal data (Sokal & Rohlf 1981). Brook et al. (2000)do not estimate confidence intervals for their extinctionriskestimates, leaving the precision <strong>of</strong> their estimates unclear.The tests <strong>of</strong> Brook et al. (2000) are applied to an ensemble<strong>of</strong> species rather than to individual species. Such atest provides information about the bias in the risk estimates,but it provides little information about their precisionbecause the expected total number <strong>of</strong> extinctionsdepends only on the average risk over the ensemble. Weillustrate this distinction with two models ( Fig. 1) basedon Tables 2 and 3 in the supplementary material <strong>of</strong> Brooket al. (2000). The first model ( Fig. 1a & 1b) is the unstructureddensity-independent growth model n(t 1) n(t)exp(r (t )) (the model used for theoretical analyses byDennis et al. [1991] and Fieberg & Ellner [2000]), withr(t) a Gaussian(, 2 ) random variable with 0.044, 0.3. The value <strong>of</strong> is a rounded average over species<strong>of</strong> the values in Brook et al.’s Table 2, and the absolutevalue <strong>of</strong> (0.044) equals the average <strong>of</strong> || overspecies. The second model (Fig. 1c & 1d) is an age-structuredLeslie matrix model with logistic density dependencein neonate survival. The mean and coefficient <strong>of</strong>variation <strong>of</strong> each vital rate for this model were derivedby taking the average <strong>of</strong> the corresponding values foreach species in Brook et al.’s Table 3, and roundingFigure 1. Results from simulatedpopulation viability analyses(PVA) using parameters based onTables 2 and 3 in the supplementarymaterial <strong>of</strong> Brook et al.(2000). (a) Comparison <strong>of</strong> observedand predicted total number<strong>of</strong> extinctions for a set <strong>of</strong> 21 species,as in Fig. 1 <strong>of</strong> Brook et al.(2000), based on the unstructuredmodel described in the text. Fivereplicates are plotted. For each <strong>of</strong>the 105 trials (21 species 5 replicates),we simulated a PVA as describedin the text. (b) Comparison<strong>of</strong> actual and estimated extinctionrisks for each <strong>of</strong> the 105 trials usedin panel (a). Actual extinction riskswere calculated by running 25,000simulations <strong>of</strong> the model using thetrue parameter values and recordingthe fraction <strong>of</strong> runs crossing beloweach estimated threshold from(a). Dashed lines show the tenthand ninetieth percentiles <strong>of</strong> the distributions<strong>of</strong> estimated extinctionrisks. (c) Comparison <strong>of</strong> observedand predicted total number <strong>of</strong> extinctions,as in panel (a), based onthe age-structured, density-dependentmodel described in the text. Allsimulations began with a populationin stable age distribution forthe mean matrix with a populationdensity <strong>of</strong> 500. (d) Comparison <strong>of</strong>actual and estimated extinctionrisks, as in panel (b), for the 105trials with the age-structured, density-dependentmodel.Conservation BiologyVolume 16, No. 1, February 2002

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