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EcoSim: Null Models Software for Ecologists

EcoSim: Null Models Software for Ecologists. Nicholas J. Gotelli Department of Biology University of Vermont Burlington, VT USA. Limitations of Ecological Data. Non-normality Small sample sizes Non-independence. Null Model Analysis. Monte Carlo simulation of ecological data

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EcoSim: Null Models Software for Ecologists

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  1. EcoSim: Null Models Software for Ecologists Nicholas J. Gotelli Department of Biology University of Vermont Burlington, VT USA

  2. Limitations of Ecological Data • Non-normality • Small sample sizes • Non-independence

  3. Null Model Analysis • Monte Carlo simulation of ecological data • Generates patterns expected in the absence of a mechanism • Allows for statistical tests of patterns • Wide applicability to community data

  4. Steps in Null Model Analysis • Define community metric X • Calculate Xobs for observed data • Randomize data subject to constraints • Calculate Xsim for randomized data • Repeat 1000 randomizations • Compare Xobs to histogram of Xsim • Measure P(Xobs£ Xsim)

  5. Niche Overlap Data

  6. Quantify Pattern as a single metric Average pairwise niche overlap = 0.17

  7. Randomize Overlap Data

  8. Null Assemblage

  9. Niche Overlap of A Single Null Community

  10. Histogram of Niche Overlaps from Null Communities

  11. Statistical Comparison with Observed Niche Overlap • Observed = 0.17

  12. Features of Null Models • Distinction between pattern/process • Possibility of no effect • Principle of parsimony • Principle of falsification • Potential importance of stochastic mechanisms

  13. Criticisms of Null Models • Ecological hypotheses cannot be stated in a way for formal proof/disproof • Interactions between factors may confound null model tests • Understanding only increased when null hypothesis is rejected • Using same data to build and test model is circular

  14. Controversy over Null Model Analysis • Early studies challenged conventional examples • Philosophical debate over falsification • Statistical debate over null model construction • Lack of powerful software

  15. EcoSim Software • Programmed in Delphi • Object-oriented design • Graphical user interface • Optimized for Windows • Supported by NSF • Created by Acquired Intelligence, Inc.

  16. Analysis of MacArthur’s (1958) warblers • 5 coexisting species of warblers in NE forests • Insectivores • Similar body sizes, diets • Paradox for classical niche theory • How could all species co-occur?

  17. MacArthur’s resolution

  18. Spatial niche segregation 2 6 25 25 25 25 25 49 18 Cape May warbler Myrtle warbler

  19. How much niche overlap of MacArthur’s warblers would be expected in the absence of species interactions?

  20. Guided Tour of EcoSim

  21. Diamond’s (1975) Assembly Rules • Not all species combinations found in nature • Those that are not found are “forbidden” • Competition and niche adjustment lead to a small number of stable species combinations

  22. Connor and Simberloff’s (1979) challenge • Assembly rules are tautologies • How much coexistence would be expected in the absence of competition • Construction of a null model to test community patterns

  23. Presence-Absence Matrix

  24. Connor and Simberloff’s (1979) null model • Species by site co-occurrence matrix • Create random matrices that maintain row totals (= species occurrences) and column totals (= number of species per site)

  25. Criticisms of C&S null model • Competitive effects “smuggled in” with row and column totals • Cannot detect certain checkerboard distributions • Constraints guarantee that simulated matrices are very similar to observed matrices

  26. Co-occurrence Analysis with EcoSim

  27. Evaluating Co-occurrence Algorithms • Type I error (incorrectly rejecting null) • Type II error (incorrectly accepting null)

  28. Evaluating Type I Error • Use null model tests on “random matrices” • A well-behaved model should reject the null hypothesis 5% of the time

  29. Evaluating Type II Error • Begin with perfectly “structured” data set • Add increasing amounts of random noise • Determine how much noise the test can tolerate and still detect non-randomness

  30. Type II Error P-value Ideal Curve 0.05 Type I Error % Noise Added

  31. Summary of Error Analyses • Best algorithm depends on co-occurrence index • Maintaining row totals (= species occurrences) necessary to control Type I error • Modified version of C&S (fixed,fixed) has low Type I, Type II errors for C-score

  32. Meta-analyses of co-occurrence • 98 presence-absence matrices from literature • analyzed for # of checkerboards, # combinations, C-score • standardized effect size using fixed,fixed null model

  33. Results • Larger C-score than expected by chance • More checkerboard species pairs than expected by chance • Fewer species combinations than expected by chance

  34. Conclusions • Published presence-absence matrices are highly non-random • Patterns match the predictions of Diamond’s assembly rules model! • Consistent with small-scale experimental studies demonstrating importance of species interactions

  35. Causes of Non-random Co-occurrence Patterns • Negative species interactions • Habitat checkerboards • Historical, evolutionary processes

  36. Statistical covariates of effect size • Number of species in matrix • Number of sites in matrix • % fill of matrix

  37. Statistical covariates of effect size • Number of species in matrix • Number of sites in matrix • % fill of matrix

  38. Biological correlates of effect size • Area (patch, geographic extent) • Insularity (island, mainland) • Biogeographic Province (Nearctic, Palearctic) • Latitude, Longitude • Taxonomic group (plants, mammals, birds)

  39. Biological correlates of effect size • Area (patch, geographic extent) • Insularity (island, mainland) • Biogeographic Province (Nearctic, Palearctic) • Latitude, Longitude • Taxonomic group (plants, mammals, birds)

  40. Ectoparasites of marine fishes Gotelli & Rohde 2002

  41. Conclusion • Homeotherm matrices highly structured • Poikilotherm matrices random co-occurrence • Ants, plant matrices highly structured • Energetic constraints may affect community co-occurrence patterns

  42. Conclusions • Null models are useful tools for analyses of community structure • Species co-occurrence in published matrices is less than expected by chance • Patterns match the predictions of Diamond’s (1975) assembly rules model • Co-occurrence patterns differ for homeotherm vs. poikilotherm matrices • EcoSim software available for analysis

  43. EcoSim Website http://homepages.together.net/~gentsmin/ecosim.htm

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