Alternative Lotka-Volterra competition

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Alternative Lotka-Volterra competition Absolute competition coefficients dN i / N i dt = r i [1 b ii N i - b ij N j ] equivalent to: dN i / N i dt = r i [K i - N i - a j N j ] / K i = r i [K i /K i - N i /K i - a j N j /K i ] = r i [1- (1/K i )N i (a j /K i )N j ]

description

Alternative Lotka-Volterra competition. Absolute competition coefficients dN i / N i dt = r i [1 – b ii N i - b ij N j ]. equivalent to: dN i / N i dt = r i [ K i - N i - a j N j ] / K i = r i [ K i / K i - N i / K i - a j N j / K i ] - PowerPoint PPT Presentation

Transcript of Alternative Lotka-Volterra competition

Page 1: Alternative  Lotka-Volterra  competition

Alternative Lotka-Volterra competition

• Absolute competition coefficients

dNi / Nidt = ri [1 – bii Ni - bij Nj]equivalent to:

dNi / Nidt = ri [Ki - Ni - aj Nj] / Ki

= ri [Ki/Ki - Ni/Ki - ajNj/Ki] = ri [1- (1/Ki)Ni – (aj/Ki)Nj]

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Absolute Lotka-Volterra

N1

0

1/b21

1/b22

dN2 / N

2dt = 0

1/b11dN

1 / N1 dt = 0

1/b12

Stable coexistence

N2

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Competitive effect vs. response

• Effect: impact of density of a species– Self density (e.g., b11)– Other species density (e.g., b21)

• Response: how density affects a species– Self density (e.g., b11)– Other species’ density (e.g., b12)

• Theory: effects differ (b11 > b21)• Experiments: responses (b11, b12)

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Absolute Lotka-Volterra

N1

0

1/b21

1/b22

dN2 / N

2dt = 0

1/b11dN

1 / N1 dt = 0

1/b12

Stable coexistence

N2

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Not ecological models• No mechanisms of competition in the model

– Phenomenological• Environment not explicitly included• Mechanistic models of Resource competition

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Resources

• component of the environment• availability increases population growth• can be depleted or used up by organisms• A resource is limiting if it determines the

growth rate of the population– Liebig’s law: resource in shortest supply

determines growth

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Resources for 0 growth

dN / N dt = 0

R*

dN / N dt > 0dN / N dt < 0

R0

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Kinds of resources

• Consider 2 potentially limiting resources• Illustrate zero growth isocline graphically• Defines 8 types• 3 types important

– substitutable– essential– switching

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Substitutable resources: Interchangeable

R2

R1

Zero growthisocline

dN / N dt < 0

dN / N dt > 0Prey for most animals

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Switching resources: One at a time

R2

R1

Zero growthisocline

dN / N dt < 0

dN / N dt > 0Nutritionallysubstitutable

Constraints onconsumption

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Essential resources: both required

R2

R1

Zero growthisocline

dN / N dt < 0

dN / N dt > 0Soil nutrientsfor plants

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Modeling resource-based population growth

• dN / N dt = p F - m– F = feeding rate on the resource– m = mortality rate (independent of R )– p = constant relating feeding to population

growth• F = FmaxR / [K1/2 + R ]

– Fmax = maximal feeding rate– K1/2 = resource level for 1/2 maximal feeding

• 1/2 saturation constant

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Feeding rate

R

F

Fmax

K1/2

• Holling type 2 Functional response

• Michaelis-Menten enzyme kinetics

• Monod microbial growth

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Modeling resource-based population growth

• dN / N dt = p FmaxR / [K1/2 + R ] - m• resource dynamics• dR / dt = a ( S - R ) - (dN / dt + mN ) c

– S = maximum resource supplied to the system

– a = a rate constant– c = resource consumption / individual

• N = 0 if S = R then dR / dt = 0

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Equilibrium

• dN / N dt = 0 and dR / dt = 0– resource consumption just balances resource

renewal– growth due to resource consumption just

balances mortality• Equilibrium resource density:

– R* = K1/2m / [ pFmax - m ]

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Limitation by 1 resource

R

dN / N dt

R*

-m

0

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Conclusion• 1 species feeding on 1 limiting resource• reduces that resource to a characteristic

equilibrium value R*

• R* determined by functional response and mortality– increases as K1/2 increases– increases as m increases– decreases as p or Fmax increase

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Two consumers competing for one resource

• dNi / Ni dt = pi Fmax iR / [K1/2 i + R ] - mi

• dR / dt = a ( S - R ) - S(dNi / dt + miNi ) ci

• each species has its own R* [ R*1 and R*

2]

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Competition for 1 resource

sp. 1

R

dN / N dt

R*1

-m1

0

R*2-m2

sp. 2

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Dynamics of competition for 1 resource

t

N

R*1

R*2

R

R

sp. 1SP.2

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Prediction for 2 species competing for 1 resource

• The species with the lower R* will eliminate the other in competition

• Independent of initial numbers• Coexistence not possible

– unless R*1 = R*

2

• R* rule

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Competitive exclusion principle

• Two species in continued, direct competition for 1 limiting resource cannot coexist

• Focus on mechanism• Coexistence (implicitly) requires 2

independently renewed resources

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Experiments

• Laboratory tests confirm this prediction• Primarily done with phytoplankton• Summarized by Tilman (1982) Grover

(1997)• Morin, pp. 40-49• Chase & Leibold, pp. 62-63

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Consumption of 2 resources

consumption vector: resultantof consumption of each resource

R1

R2 Ci1

Ci2Ci

consumes more R1

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Essential resources

consumption vectors are parallel(essential)

R1

R2 Ci1

Ci2C1

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Substitutable resources

consumption vectors are not parallel(substitutable)

R1

R2 Ci1

Ci2Ci

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Switching resources

consumption vectors are perpendicularto isocline(switching)

R1

R2

C1

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Renewal for 2 resources

supply vector: points at supplypoint S1,S2

R1

R2

S1,S2

U

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Equilibrium: 1 sp. 2 resources

consumption vector equal &opposite supplyvector

R1

R2

Ci

Ci

Ci

U

S1,S2

UU

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Equilibrium

• Equilibrium (R1,R2) falls on isocline• therefore, dN / N dt =0• U and C vectors equal in magnitude,

opposite direction• therefore dR1 / dt = 0 and dR2 / dt = 0

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Competition for 2 resources

R1

R2

sp. 1

S1,S2

S1,S2

S1,S2

sp. 2

sp. 1 alwaysexcludes sp. 2

sp. 2 cannotsurvive

neither spp.can survive

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Competition for 2 resources

R1

R2

S1,S2

S1,S2

S1,S2 neither spp.

can survive

sp. 2 cannotsurvive

sp. 1 alwaysexcludes sp. 2

S1,S2

coexistence

sp. 1

sp. 2

sp. 2

sp. 1

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Equilibrium• sp. 1

– needs less R1 (limited by R2)– consumes more R2

• sp. 2– needs less R2 (limited by R1)– consumes more R1

• consumes more of the resource limiting to itself