Appendix S1 Density-dependent resource selection by a terrestrial herbivore in response to sea-to-land nutrient transfer by seals PHILIP D. MCLOUGHLIN1,*, KENTON LYSAK1, LUCIE DEBEFFE1, THOMAS PERRY1, AND KEITH A. HOBSON2,3 1 Department of Biology, University of Saskatchewan, 112 Science Place, Saskatoon, SK S7N 5E2, Canada 2 Environment Canada, 11 Innovation Boulevard, Saskatoon, SK S7N 3H5, Canada 3 Department of Biology, University of Western Ontario, London, ON N6A 5B7, Canada 2 APPENDIX S1. Spatial heterogeneity in sea-to-land nutrient subsidization leading to increased persistence of consumer populations on islands via density-dependent habitat or resource selection. The process of adaptive resource or habitat selection is well described by concepts like the idealfree distribution (Fretwell and Lucas 1969) and related fitness-maximizing models of space use (reviews in Rosenzweig 1981, 1991; Morris 2003). Optimizing behavior of individuals to acquire resources may be especially important for terrestrial population dynamics and community stability in the context of allochthonous nutrient transfers because: 1) inputs on islands are expected to be spatially variable (concentrated around colonies of animal vectors or shorelines), which may then promote fine-scale heterogeneity (patchiness) in local carrying capacities of consumers and out-of-phase population dynamics (Coulson et al. 1997); and 2) density- and habitat-dependent mixing of behavioral strategies by consumers to optimally select resources should contribute to periodic movements and spatial genetic admixture (Fortin et al. 2008). For example, we can imagine the role of density-dependent habitat selection in driving dynamics of a ‘patchy metapopulation’ (Harrison 1991) among regions of an island where seabird colonies fertilize discrete ornithogenic pastures that drive local dynamics (Fig. S1). Presence of enrichment will lead to direct or indirect increases in density of food or limiting nutrients for terrestrial consumers at or near these patches. Population dynamics of island consumers (secondary or tertiary) will thus tend towards that of a patchy metapopulation, whereby subpopulations linked to patches are sufficiently close to function as a single population yet differences in dynamics may exist due to stochasticity or, in this case, behavior of fitnessmaximizing individuals. For the latter, individuals will preferentially occupy different patches as 3 density increases locally, depending on quality of patches and dispersal costs following expectations of density-dependent habitat selection (e.g., via ideal-free distribution when no costs to movement are involved, or density-dependent habitat selection with costs to movement [Rosenzweig 1981, 1991; Morris 1987, 2003; Fig. S1]). The overall effect of spatial heterogeneity in sea-to-land nutrient transfer paired with behavioral strategies to select resources in a fitness-maximizing manner is to increase persistence probability of a consumer which exists as a patchy population (Harrison 1991), or by extension allow for species coexistence of competitors and/or a predator and its prey, as expected from metapopulation theory (Hanski and Gilpin 1991). Figure S1. Patches (a, b, c) can be described by fitness isodars of associated consumer densities (pairwise plots of densities, see Morris [1987, 2003]). Regions of the model island are linked by 4 patch dynamics through dispersal in response to competition (broad arrows). Density-dependent costs of emigration from one area to another and perceived changes in quality amongst areas in density-dependent fashion relates to slope of isodars (Morris 1987), with ideal-free distribution (and no cost of dispersal) conveyed by slope 1.0 (dashed line) but non-zero intercept (as for pairing a-c). For pairings (a-b) and (b-c) there is a density-dependent emigration cost, e.g., habitat (a) is perceived to decrease in quality relative to habitat (b) in a density-dependent fashion (with expected net migration towards b, as indicated by broad arrows), fitness-density curves are convergent and the isodar slope < 1.0 (vice-versa for pairing b-c). Background including relevant equations in Morris (1987, 2003). LITERATURE CITED Coulson, T., S. Albon, F. Guinness, J. Pemberton, and T. Clutton-Brock. 1997. Population substructure, local density, and calf winter survival in red deer (Cervus elaphus). Ecology 78: 852–863. Fortin, D., D. Morris, and P.D. McLoughlin. 2008. 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