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Patch dynamics in a landscape modified by ecosystem engineers

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ConclusionsThe set of models developed here helps l<strong>in</strong>k thepopulation <strong>dynamics</strong> of <strong>ecosystem</strong> eng<strong>in</strong>eers to the<strong>dynamics</strong> of the patches that they create. By predict<strong>in</strong>gthe relative abundance of eng<strong>in</strong>eered and uneng<strong>in</strong>eeredpatches <strong>in</strong> a <strong>landscape</strong>, it has the potential to serve as animportant tool <strong>in</strong> determ<strong>in</strong><strong>in</strong>g the effects of <strong>ecosystem</strong>eng<strong>in</strong>eers on <strong>ecosystem</strong> structure and function at the<strong>landscape</strong> scale. Application of the model to a populationof beaver <strong>in</strong> the central Adirondack Mounta<strong>in</strong>ssuggests that because successful colonization rates arelow and site abandonment rates are high, the populationpersistence may depend on dispersers from beavercolonies <strong>in</strong> un<strong>modified</strong> patches such as natural lakes.Although we are not aware of any data set that wouldallow for complete parameterization of the model,analysis of the model suggests a number of possibletests of its structure and assumptions. The model makesnumerous testable predictions about how the distributionof patch types <strong>in</strong> a <strong>landscape</strong> should change <strong>in</strong>response to changes <strong>in</strong> the population <strong>dynamics</strong> ofeng<strong>in</strong>eers or the recovery rate of patches after theyhave been abandoned. Furthermore, <strong>by</strong> comb<strong>in</strong><strong>in</strong>g thismodel with an understand<strong>in</strong>g of how <strong>ecosystem</strong> eng<strong>in</strong>eer<strong>in</strong>gaffects diversity at the <strong>landscape</strong> scale, we nowhave the tools to relate the population <strong>dynamics</strong> of anorganism to patterns of <strong>landscape</strong>-level diversity.Acknowledgements / The authors gratefully acknowledge theAdirondack Ecological Center for access to the long-term dataset on beaver <strong>dynamics</strong> of the Hunt<strong>in</strong>gton Wildlife Forest.Special thanks to C. Demers and R. Sage for their help <strong>in</strong>organiz<strong>in</strong>g and ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g this valuable resource. A. Flecker, P.Marks, B. Goodw<strong>in</strong>, R. Root and P. Nummi provided manyuseful comments and suggestions for improv<strong>in</strong>g the manuscript.This work was funded <strong>by</strong> Sigma Xi, the Laurel Foundation, theKieckhefer Adirondack Fellowship, the Institute of EcosystemStudies, and an NSF GRT for Human AcceleratedEnvironmental Change. This study is a contribution to theInstitute of Ecosystem Studies.ReferencesBarnes, W. J. and Dibble, E. 1986. The effects of beaver <strong>in</strong>riverbank forest succession. / Can. J. Bot. 66: 40/44.Beer, J. R. 1955. Movements of tagged beaver. / J. Wildl.Manage. 19: 492/493.Bergerud, A. T. and Miller, D. R. 1977. Population <strong>dynamics</strong> ofNewfoundland beaver. / Can. J. Zool. 55: 1480/1492.Coleman, F. C. and Williams, S. L. 2002. Overexploit<strong>in</strong>g mar<strong>in</strong>e<strong>ecosystem</strong> eng<strong>in</strong>eers: potential consequences for biodiversity./ Trends Ecol. Evol. 17: 40/43.Coll<strong>in</strong>s, S. L. and Uno, G. E. 1983. 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