1 / 52

Edmund M. Hart and Nicholas J. Gotelli Department of Biology The University of Vermont

Modeling Metacommunities : A comparison of Markov matrix models and agent-based models with empirical data. Edmund M. Hart and Nicholas J. Gotelli Department of Biology The University of Vermont. Talk Overview. Objective Introduction to coexistence models Model system overview

umed
Download Presentation

Edmund M. Hart and Nicholas J. Gotelli Department of Biology The University of Vermont

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Modeling Metacommunities: A comparison of Markov matrix models and agent-based models with empirical data Edmund M. Hart and Nicholas J. Gotelli Department of Biology The University of Vermont

  2. Talk Overview • Objective • Introduction to coexistence models • Model system overview • Markov matrix model methods • Agent based model (ABM) methods • Comparison of model results and empirical data • Comparison of modeling methods

  3. Objective • To use community assembly rules to construct a Markov matrix model and an ABM to generate models of species coexistence. • Compare two different methods for modeling metacommunities to empirical data to assess their performance. • Can simple rules be used to accurately model real systems?

  4. How do species coexist?

  5. Classical models and their multispecies expansions (eg Chesson 1994) Lotka-Volterra Competition Model N2 N1

  6. Mechanisms to Enhance Coexistence in Closed Communities • Environmental Complexity Niche dimensionality, Spatial refuges • Multispecies Interactions Indirect effects • Complex Two-Species Interactions Intra-Guild Predation, Ratio of inter to intra specific competition • Neutral models Unstable coexistence and ecological drift

  7. But what about space?

  8. Classical spatial models Levins patch-occupancy metapopulation model All population vital rates are condensed into probability of immigration and extinction

  9. Metacommunity models • Models in spatially homogenous resources • Patch-dynamics • Life history trade-offs, e.g. competition-colonization • Trade-offs allow spatial niche-differences along a single resource niche axis • Neutral models • All species are equivalent, no trade-offs • Differences in community structure come from ecological drift and speciation.

  10. Metacommunity models • Models in spatially heterogenous resources • Species sorting • Local dynamics on a different time scale than regional colonization events • Similar to classical niche-theory, communities are stable and colonization not so frequent that species persist in sinks • Mass effects • A multi-species source sink model, local and regional dynamics on similar time scales • Asymmetric dispersal from spatial storage effects enhances local birth rates

  11. Can we model metacommunity structure using community assembly rules?

  12. A Minimalist Metacommunity P N1 N2

  13. A Minimalist Metacommunity P Top Predator N1 N2 Competing Prey

  14. MetacommunitySpecies Combinations Ѳ N1 N2 P N1N2 N1P N2P N1N2P

  15. Testing Model Predictions

  16. Actual data Species occurrence records for tree hole #2 recorded biweekly from 1978-2003(!)

  17. Actual data Toxorhynchitesrutilus P Ochlerotatustriseriatus Aedesalbopictus N1 N2

  18. Markov matrix models

  19. Stage at time (t) • = Stage at time (t + 1)

  20. “Community” “Patch”

  21. Community Assembly Rules • Single-step assembly & disassembly • Single-step disturbance & community collapse • Species-specific colonization potential • Community persistence (= resistance) • Forbidden Combinations & Competition Rules • Overexploitation & Predation Rules • Miscellaneous Assembly Rules

  22. Competition Assembly Rules • N1 is an inferior competitor to N2 • N1 is a superior colonizer to N2 • N1 N2 is a “forbidden combination” • N1 N2 collapses to N2 or to 0, or adds P • N1 cannot invade in the presence of N2 • N2 can invade in the presence of N1

  23. Predation Assembly Rules • P cannot persist alone • P will coexist with N1 (inferior competitor) • P will overexploit N2 (superior competitor) • N1 can persist with N2 in the presence of P

  24. Miscellaneous Assembly Rules • Disturbances relatively infrequent (p = 0.1) • Colonization potential: N1 > N2 > P • Persistence potential: N1 > PN1 > N2 > PN2 > PN1N2 • Matrix column sums = 1.0

  25. Complete Transition Matrix

  26. Testing Model Predictions

  27. Markov matrix model output

  28. Agent based modeling methods

  29. Pattern Oriented Modeling • Use patterns in nature to guide model structure (scale, resolution, etc…) • Use multiple patterns to eliminate certain model versions • Use patterns to guide model parameterization

  30. ABM Assembly Rules • N1 is an inferior competitor to N2 • N1 is a superior colonizer to N2 • N1 N2 is a “forbidden combination” • N1 N2 collapses to N2 or to 0, or adds P • N1 cannot invade in the presence of N2 • N2 can invade in the presence of N1 • P cannot persist alone • P will coexist with N1 (inferior competitor) • P will overexploit N2 (superior competitor) • N1 can persist with N2 in the presence of P • Disturbances relatively infrequent (p = 0.1) • Colonization potential: N1 > N2 > P

  31. ABM example

  32. Randomly generated metacommunity patches by ABM • 150 x 150 randomly generated • metacommunity, patches are • between 60 and 150 cells, with a • minimum buffer of 15 cells. • Initial state of 100 N1 and N2 and 75 P • all randomly placed on habitat patches. • All models runs had to be 2000 time steps long in order to be analyzed.

  33. ABM Output

  34. ABM Output

  35. Testing Model Predictions

  36. ABM community frequency output The average occupancy for all patches of 10 runs of a 25 patch metacommunity for 2000 times-steps

  37. Testing Model Predictions

  38. Why the poor fit? – Markov models “Forbidden combinations”, and low predator colonization High colonization and resistance probabilities dictated by assembly rules

  39. Why the poor fit? – ABM Species constantly dispersing from predator free source habitats allowing rapid colonization of habitats, and rare occurence of single species patches Predators disperse after a patch is totally exploited

  40. Metacommunity dynamics of mosquitos Ellis et al found elements of life history trade offs, but also strong correlations between species and habitat, indicating species-sorting Ellis, A. M., L. P. Lounibos, and M. Holyoak. 2006. Evaluating the long-term metacommunity dynamics of tree hole mosquitoes. Ecology 87: 2582-2590.

  41. Advantages of each model

  42. Disadvantages of each model

  43. Concluding thoughts… • Models constructed using simple assembly rules just don’t cut it. • Need to parameretized with actual data or have a more complicated set of assumptions built in. • Using similar assembly rules, Markov models and ABM’s produce different outcomes. • Differences in how space and time are treated • Differences in model assumptions (e.g. immigration) • Given model differences, modelers should choose the right method for their purpose

  44. ABM Parameterization

  45. Acknowledgements Markov matrix modeling Nicholas J. Gotelli– University of Vermont Mosquito data Phil Lounibos – Florida Medical Entomology Lab Alicia Ellis - University of California – Davis Computing resources James Vincent – University of Vermont Vermont Advanced Computing Center

More Related