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[Population dynamics] Population dynamics
Pattern of change in population size over time
[Population dynamics] Hare-lynx cycle
Classic ~10-year population cycle
[Population dynamics] Best explanation for hare-lynx cycles
A combination of food limitation and predator limitation
[Population dynamics] Discrete-time growth
N(t+1) as a function of N(t)
[Population dynamics] Continuous-time growth
dN/dt = limit of change in N over change in t as delta t approaches 0; N grows if dN/dt > 0 and shrinks if < 0
[Lotka-Volterra] Prey equation
dN/dt = rN - aNP
[Lotka-Volterra] Predator equation
dP/dt = baNP - mP
[Lotka-Volterra] N
Prey population density
[Lotka-Volterra] P
Predator population density
[Lotka-Volterra] r
Intrinsic (exponential) growth rate of prey without predators
[Lotka-Volterra] a
Attack rate
[Lotka-Volterra] aNP
Rate prey are eaten; mass action (encounters proportional to N times P)
[Lotka-Volterra] b
Conversion rate of eaten prey into predator reproduction
[Lotka-Volterra] baNP
Predator population growth from eating prey
[Lotka-Volterra] m
Predator mortality rate
[Lotka-Volterra] rN term
Prey natural population growth (+)
[Lotka-Volterra] mP term
Predator natural mortality (-)
[Lotka-Volterra] What happens with no predators (P = 0)?
Prey grow exponentially
[Lotka-Volterra] What happens with a = 0?
Prey grow exponentially and predators go extinct
[Lotka-Volterra] Key assumption of simple LV model
Prey experience no food limitation (no carrying capacity)
[Lotka-Volterra] Typical LV output
Coupled oscillations with predator peaks lagging prey peaks
[Lotka-Volterra] Why is LV still useful?
Simple way to think about predator-prey interactions and their dynamics even though it doesn't fully explain hare-lynx cycles
[Lotka-Volterra] Individual-based models
Simulate consumption, reproduction and death of individuals using rules instead of equations; give similar results (e.g., NetLogo)
[Lotka-Volterra] Rosenzweig-MacArthur [Extra]
LV plus prey carrying capacity and predator saturation (type II functional response); can produce stable equilibria or limit cycles
[Lotka-Volterra] Paradox of enrichment
Making a system more productive increases oscillation amplitude and can lead to predator extinction
[Lotka-Volterra] Paradox of enrichment consequence
Highly productive environments can be less diverse than less productive ones
[Activity 3] Default NetLogo dynamics
Cycles: sheep rise, wolves rise, wolves overeat sheep and starve, cycle repeats; grass opposes sheep
[Activity 3] Slider matching r
sheep-reproduce (sheep reproduction without predators)
[Activity 3] Slider matching b
wolf-gain-from-food (energy wolves gain per sheep); alternate candidate wolf-reproduce
[Activity 3] 50 sheep and 250 wolves
Wolves crash early, sheep drop drastically (often both fail) because too many wolves overconsume prey
[Activity 3] Why did 50 sheep/250 wolves crash?
Wolves overconsume sheep, don't gain enough energy to reproduce, and starve when sheep become scarce
[Activity 3] Wolf reproduction to 20%
Cycle amplitude increases; higher extremes in wolf numbers
[Activity 3] Why can wolves go extinct at high reproduction?
Wolves grow fast, wipe out sheep, then starve with few survivors
[Activity 3] wolf-gain-from-food = 0
Sheep increase, grass decreases, then both stabilize with many sheep and little grass
[Activity 3] Trophic cascade in wolf-sheep-grass
Wolves don't eat grass but indirectly protect it by reducing sheep
[Activity 3] Lowering grass-regrowth-time (first effect)
Amplitude of oscillations of all three populations increases
[Activity 3] Lowering grass-regrowth-time (eventual effect)
Wolves go extinct
[Activity 3] After wolves vanish
Sheep rise then stabilize; grass limits sheep; grass and sheep slowly oscillate around stable values
[Activity 3] Is the system more or less stable after wolf loss?
Less stable (bigger oscillations) and lower biodiversity