Dispersal Landscape Ecology Definitions Dispersal ◦ Spreading of individuals away from others Migration ◦ Mass directional movements of large numbers of species from one location to another. Question/Comments Do all species disperse? Yes… ◦ Some by choice, some by chance Chance can be influenced by evolution. E.g. dandelions sees are puffy for a “reason”. Dispersal Why disperse? ◦ Escape immediate environment. Relieve local congestion. ◦ Discovery Dispersal 1) Exploring, picking, then settling 2) Exploring, staying. ◦ Non-discovery dispersal Matter of change, e.g. seeds. Do animal moves randomly? Random Correlated random walk Memory – making a decision. Does it depend on patch type? Do animal moves randomly? Usually no…. ◦ But that is as individuals, do they as a group? Examples – Fire Ants European Starling How to model this spread? What do we need to know about a population? ◦ How far they move? ◦ How fast the population grows? ◦ Suitable Habitat? Integrodifference Equation Types of model? Scientific or Statistical? Analytical or Simulation? Static or dynamic? Modified diffusion equation How to model this spread? Diffusion equation? 2004 Distribution Reservoirs in OK and KS in Verdigis River basin Lake Mead & Havasu 80 100 120 Inland Lake Distance to Great Lakes 60 Frequency 2400 60 80 Inland Lake Distance to 1993 Distribution 40 quency 1700 Gravity Models – primary spread from the Great Lakes Scaling Factor K U A O W D ij i 1 d i i j ij Area Number of Boats Distance & coefficient Types of model? Scientific or Statistical? Analytical or Simulation? Static or dynamic? United States Gravity Model Basic Information ◦ Based on 210 Watersheds ◦ Estimate # of boaters/watershed ◦ Sum lake area/watershed How to parameterize? ◦ Boat surveys ◦ Local information Primary Question – ◦ How many boaters from areas with zebra mussels are traveling to western waters? United States Gravity Model From Bossenbroek et al. 2007 Conservation Biology From Bossenbroek et al. 2007 Conservation Biology 2007 Distribution Predict the spread of emerald ash borer Local Dispersal Human-mediated Dispersal Modeling Dispersal Natural Spread Linear Distance Yr 1 Yr 2 Yr 3 Time Modeling Dispersal Long-distance spread Yr 1 Yr 3 Linear Distance Yr 2 Time Predict the spread of emerald ash borer Does natural dispersal account for the rapidity with which the emerald ash borer has spread, even at the county scale? Diffusion Modeling Used a derivation of Skellam’s diffusion equation Toledo N N N f ( N ) D 2 2 t y x 2 2 2004 VF 4rD Croskey 2009 - Thesis Can diffusion explain this rate of movement? 2005 Estimating Diffusion Model Parameters VF = velocity of the invasion front ◦ Observed in Lucas County Ohio 16 – 40 km/year D = diffusion coefficient VF 4rD ◦ Reported movement capabilities of EAB 0.8 – 20 km/year r = intrinsic rate of increase ◦ r values for other beetles 0.1 – 9.1 Force the model to fit observations by solving for r and D Croskey 2009 - Thesis Diffusion Model Alone Cannot Explain EAB Spread When D is estimated (obs = 0.8 – 20 km/year) mean = 802.80 km/year When r is estimated (obs = 0.1 – 9.0 ): mean = 76.04 Natural dispersal is not responsible for the rate at which the emerald ash borer has spread Croskey 2009 - Thesis Predict the spread of emerald ash borer Develop models for both: ◦ Local Dispersal ◦ Human-mediated Dispersal Natural (or local) Dispersal of EAB in Ohio Prasad et al. 2010 Predict the spread of emerald ash borer Local Dispersal ◦ Flight (~2 km/yr) ◦ Local human spread (~20 km/yr) Human-mediated dispersal ◦ Campers moving firewood ◦ Hitchhikers on cars, trucks, etc. i.e. road networks. ◦ Wood products industry Predict the spread of emerald ash borer: Human-mediated dispersal K U A O W ij i i jD ij d i 1 Campers with Firewood Bossenbroek & Jerde – in review Natural and HumanMediated Dispersal of EAB in Ohio Prasad et al. 2010 Compared model to known distribution Examined the model predictions to the patterns of the human factors included. We examined 11 of the major routes from Detroit, MI, to major cities in Ohio ◦ And included one turn only onto an adjoining highway. ◦ Then buffered these highways at 1, 2, and 4 km. Results: ◦ 52% of the known locations of EAB fell within 1 km ◦ 64% fell within 2 km ◦ 81% fell within 4 km these few roads that represent only 34.7% of the total road length used in the modeling. Prasad et al. 2010. This result highlights the importance of the role of major highways that are in a connected road network in spreading the emerald ash borer.