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The quantitative study of marked individuals in ecology, evolution ...

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EURING 2003 Radolfzell<br />

among parameters are preserved. We comb<strong>in</strong>e Bayesian analysis and <strong>in</strong>tegrated<br />

analysis to develop a population dynamics model for the eastern Pacific Ocean (EPO)<br />

spotted dolph<strong>in</strong>. <strong>The</strong> model is developed to <strong>in</strong>clude the various types <strong>of</strong> data that are<br />

available for this population. Informative priors are <strong>in</strong>cluded for several model parameters.<br />

Forward projections are used to <strong>in</strong>vestigate different management options.<br />

04:55 PM - 05:20 PM<br />

Application <strong>of</strong> Bayesian decision mak<strong>in</strong>g and MCMC to the conservation <strong>of</strong> a harvested<br />

species<br />

Chris Fonnesbeck & Mike Conroy<br />

When endeavor<strong>in</strong>g to make <strong>in</strong>formed decisions, conservation biologists must frequently<br />

contend with disparate sources <strong>of</strong> data and compet<strong>in</strong>g hypotheses about the<br />

likely impacts <strong>of</strong> proposed decisions on the resource's status. Frequently, statistical<br />

analyses, model<strong>in</strong>g (e.g., for population projection) and optimization or simulation to<br />

<strong>in</strong>vestigate candidate alternative decisions, are conducted as separate exercises. For<br />

example, a population model might be constructed, whose parameters are then estimated<br />

from data (e.g., r<strong>in</strong>g<strong>in</strong>g studies, population surveys); f<strong>in</strong>ally, the parameterized<br />

model might then be used to <strong>in</strong>vestigate alternative candidate decisions, via simulation,<br />

optimization, or both. This approach, while effective, does not take full advantage<br />

<strong>of</strong> the <strong>in</strong>tegration <strong>of</strong> data and model components for prediction and updat<strong>in</strong>g; we propose<br />

a Bayesian context to provide this <strong>in</strong>tegration.<br />

In the case <strong>of</strong> American black ducks (Anas rubripes) managers are simultaneously<br />

faced with try<strong>in</strong>g to extract a susta<strong>in</strong>able harvest from the species, while ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g<br />

<strong>in</strong>dividual stocks above acceptable thresholds. <strong>The</strong> problem is complicated by spatial<br />

heterogeneity <strong>in</strong> the growth rates and carry<strong>in</strong>g capacity <strong>of</strong> black ducks stocks, movement<br />

between stocks, regional differences <strong>in</strong> the <strong>in</strong>tensity <strong>of</strong> harvest pressure, and<br />

heterogeneity <strong>in</strong> the degree <strong>of</strong> competition from a close congener, mallards (Anas<br />

platyrynchos) among stocks. We have constructed a population life cycle model that<br />

takes these components <strong>in</strong>to account and simultaneously performs parameter estimation<br />

and population prediction <strong>in</strong> a Bayesian framework. R<strong>in</strong>g<strong>in</strong>g data are used to<br />

develop posterior predictive distributions for harvest mortality rates, given as <strong>in</strong>put<br />

decisions about harvest regulations. Population surveys <strong>of</strong> black ducks and mallards<br />

are used to obta<strong>in</strong> stock-specific estimates <strong>of</strong> population size for both species, for <strong>in</strong>puts<br />

<strong>in</strong>to the population life-cycle model. <strong>The</strong>se estimates are comb<strong>in</strong>ed with the posterior<br />

distributions for harvest mortality, to obta<strong>in</strong> posterior predictive distributions <strong>of</strong><br />

future population status for candidate sets <strong>of</strong> regional harvest regulations, under alternative<br />

biological hypotheses for black duck population dynamics. <strong>The</strong>se distributions<br />

are then used both for the exploration <strong>of</strong> optimal harvest policies and for sequential<br />

updat<strong>in</strong>g <strong>of</strong> model posteriors, via comparison <strong>of</strong> predictive distributions to future<br />

survey estimates <strong>of</strong> stock-specific abundance. Our approach illustrates advantages <strong>of</strong><br />

MCMC for <strong>in</strong>tegrat<strong>in</strong>g disparate data sources <strong>in</strong>to a common predictive framework, for<br />

use <strong>in</strong> conservation decision mak<strong>in</strong>g.<br />

05:20 PM - 05:45 PM<br />

Decision models for the optimal management <strong>of</strong> biodiversity trust fund<br />

Mart<strong>in</strong> Drechler & Frank Wätzold<br />

<strong>The</strong> conservation <strong>of</strong> species generally requires long-last<strong>in</strong>g commitments over many<br />

years or decades. Even though technically, management plans can be designed for<br />

such long timeframes their practical implementation is constra<strong>in</strong>ed by the future<br />

25

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