Appendix S1: Considerations for developing robust gb models 2 Appendix S2: Sensitivity Analysis 5 Table summary of Sensitivity Analysis on Parameters 11 Table summary of Sensitivity Analysis on Model Assumptions 12 Figure S1
Appendix S3: Additional Data and Analysis
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- Table S4: LULC Reclassifications
- Figure S19. Seed dispersal kernel estimates
Appendix S3: Additional Data and AnalysisTable S3. Growth Rate and Habitat Use Data
Summary of data used to parameterize habitat use for European starlings and Oriental bittersweet. The proportion of landscape was evaluated for the region where radio tracking was conducted (LaFleur 2006). Plant survival and mean dry weight biomass was measured across replicate sites from a transplant experiment (seedlings: LaFleur unpublished; adults: Leicht 2005). Bold values are model parameters estimated from data. Table S4: LULC ReclassificationsDefinitions of the reclassification scheme used to translate NOAA data for the model.
Figure S19. Seed dispersal kernel estimatesWe used radio tracking data to estimate local bird movements and banding recaptures to estimate larger scale movements in conjunction with gut passage time to produce a seed dispersal kernel. Shown are three characteristic seed retention times (that represent the range) coupled with both local and banding data. We produced a conservative envelop around the kernel chosen for the model (dark line). The inset histogram shows the frequency distribution of the distances traveled by starlings between banding and recapture over an intervals of two days or less. The proportion of seeds deposited in each cell by the kernel chosen for the model (dark line) is shown along the horizontal axis. 
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