4.7 Article

Statistical power for detecting trends with applications to seabird monitoring

Journal

BIOLOGICAL CONSERVATION
Volume 111, Issue 3, Pages 317-329

Publisher

ELSEVIER SCI LTD
DOI: 10.1016/S0006-3207(02)00301-4

Keywords

Alaska; biological significance; components of variance; computer software; exponential models; linear regression; pseudoreplication; seabird monitoring; statistical power; study design; time series; trend analysis

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Power analysis is helpful in defining goals for ecological monitoring and evaluating the performance of ongoing efforts. I examined detection standards proposed for population monitoring of seabirds using two programs (MONITOR and TRENDS) specially designed for power analysis of trend data. Neither program models within- and among-years components of variance explicitly and independently, thus an error term that incorporates both components is an essential input. Residual variation in seabird counts consisted of day-to-day variation within years and unexplained variation among years in approximately equal parts. The appropriate measure of error for power analysis is the standard error of estimation (S.E.(est)) from a regression of annual means against year. Replicate counts within years are helpful in minimizing S.E-(est) but should not be treated as independent samples for estimating power to detect trends. Other issues include a choice of assumptions about variance structure and selection of an exponential or linear model of population change. Seabird count data are characterized by strong correlations between S.D. and mean, thus a constant CV model is appropriate for power calculations. Time series were fit about equally well with exponential or linear models, but log transformation ensures equal variances over time, a basic assumption of regression analysis. Using sample data from seabird monitoring in Alaska, I computed the number of years required (with annual censusing) to detect trends of -1.4% per year (50% decline in 50 years) and -2.7% per year (50% decline in 25 years). At alpha = 0.05 and a desired power of 0.9, estimated study intervals ranged from I I to 69 years depending on species, trend, software, and study design. Power to detect a negative trend of 6.7% per year (50% decline in 10 years) is suggested as an alternative standard for seabird monitoring that achieves a reasonable match between statistical and biological significance. Published by Elsevier Science Ltd.

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