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Chilean Blue Whales as a Case Study to Illustrate Methods to Estimate Abundance and Evaluate Conservation Status of Rare Species
Authors:ROB WILLIAMS  SHARON L HEDLEY  TREVOR A BRANCH  MARK V BRAVINGTON  ALEXANDRE N ZERBINI  KEN P FINDLAY
Institution:1. Canada‐US Fulbright Visiting Research Chair, Jackson School, University of Washington, Seattle, WA 98195, U.S.A.;2. Centre for Research into Ecological and Environmental Modelling, The Observatory, Buchanan Gardens, University of St. Andrews, St. Andrews, Fife KY16 9LZ, United Kingdom;3. School of Aquatic and Fishery Sciences, Box 355020, University of Washington, Seattle, WA 98195, U.S.A.;4. CSIRO Mathematical and Information Sciences, Marine Laboratories, Castray Esplanade, GPO Box 1538 Hobart, Tasmania 7001, Australia;5. National Marine Mammal Laboratory, Alaska Fisheries Science Center/NOAA, 7600 Sand Point Way NE, Seattle, WA 98115‐6349, U.S.A.;6. Cascadia Research Collective, 218 1/2 W 4th Avenue, Olympia, WA 98501, U.S.A.;7. Oceanography Department, University of Cape Town, Private Bag, Rondebosch 7701, South Africa
Abstract:Abstract: Often abundance of rare species cannot be estimated with conventional design‐based methods, so we illustrate with a population of blue whales (Balaenoptera musculus) a spatial model‐based method to estimate abundance. We analyzed data from line‐transect surveys of blue whales off the coast of Chile, where the population was hunted to low levels. Field protocols allowed deviation from planned track lines to collect identification photographs and tissue samples for genetic analyses, which resulted in an ad hoc sampling design with increased effort in areas of higher densities. Thus, we used spatial modeling methods to estimate abundance. Spatial models are increasingly being used to analyze data from surveys of marine, aquatic, and terrestrial species, but estimation of uncertainty from such models is often problematic. We developed a new, broadly applicable variance estimator that showed there were likely 303 whales (95% CI 176–625) in the study area. The survey did not span the whales' entire range, so this is a minimum estimate. We estimated current minimum abundance relative to pre‐exploitation abundance (i.e., status) with a population dynamics model that incorporated our minimum abundance estimate, likely population growth rates from a meta‐analysis of rates of increase in large baleen whales, and two alternative assumptions about historic catches. From this model, we estimated that the population was at a minimum of 9.5% (95% CI 4.9–18.0%) of pre‐exploitation levels in 1998 under one catch assumption and 7.2% (CI 3.7–13.7%) of pre‐exploitation levels under the other. Thus, although Chilean blue whales are probably still at a small fraction of pre‐exploitation abundance, even these minimum abundance estimates demonstrate that their status is better than that of Antarctic blue whales, which are still <1% of pre‐exploitation population size. We anticipate our methods will be broadly applicable in aquatic and terrestrial surveys for rarely encountered species, especially when the surveys are intended to maximize encounter rates and estimate abundance.
Keywords:abundance  Balaenoptera musculus  distance sampling  line transect  rare  spatial model  variance  abundancia  Balaenoptera musculus  modelo espacial  muestreo a distancia  transecto lineal  raro  varianza
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