Gause, Luckinbill, Veilleux, and What to Do. Christopher X Jon Jensen Stony Brook University

Similar documents
The Paradox of Enrichment:

Are the prey- and ratio-dependent functional responses really extremes along a continuum of predator interference?

Li et al submitted to Proc Roy Soc B: Reconsidering delay dependent models

Effect of Species 2 on Species 1 Competition - - Predator-Prey + - Parasite-Host + -

Community Ecology. Classification of types of interspecific interactions: Effect of Species 1 on Species 2

Linked exploitation and interference competition drives the variable behavior of a classic predator prey system

Chapter 11: Species Interactions II - Predation

Ecology 302: Lecture VII. Species Interactions.

Interspecific Competition

dv dt Predator-Prey Models

D. Correct! Allelopathy is a form of interference competition in plants. Therefore this answer is correct.

THETA-LOGISTIC PREDATOR PREY

Chapter 16: Competition. It s all mine, stay away!

BIO 114 Spring Protozoan Population Ecology and Interactions

1. Population dynamics of rabbits and foxes

Lecture 20/Lab 21: Systems of Nonlinear ODEs

Predation. Predation & Herbivory. Lotka-Volterra. Predation rate. Total rate of predation. Predator population 10/23/2013. Review types of predation

EXPERIMENTAL DEMONSTRATION OF VOLTERRA'S PERIODIC OSCILLATIONS IN THE NUMBERS OF ANIMALS

Field experiments on competition. Field experiments on competition. Field experiments on competition

Predation is.. The eating of live organisms, regardless of their identity

BIOL 410 Population and Community Ecology. Predation

Ecology Regulation, Fluctuations and Metapopulations

A New Human Predation Model for Late Pleistocene Megafaunal Extinction Patterns in North America

Age (x) nx lx. Population dynamics Population size through time should be predictable N t+1 = N t + B + I - D - E

Ecology 203, Exam III. November 16, Print name:

Interactions between predators and prey

Name Student ID. Good luck and impress us with your toolkit of ecological knowledge and concepts!

Lecture 12. Chapter 10: Predator Prey interactions Chapter 11: Plant Herbivore interactions

Chapter 6 Population and Community Ecology

Parameter Sensitivity In A Lattice Ecosystem With Intraguild Predation

Coupling in Predator-Prey Dynamics: Ratio-Dependence

Chapter 6 Population and Community Ecology. Thursday, October 19, 17

Chapter 6 Reading Questions

Ordinary Differential Equations

EFFECT OF RESOURCE ENRICHMENT ON A CHEMOSTAT COMMUNITY OF BACTERIA AND BACTERIOPHAGE

COMPETITION OF FAST AND SLOW MOVERS FOR RENEWABLE AND DIFFUSIVE RESOURCE

BIOS 5445: Human Ecology Dr. Stephen Malcolm, Department of Biological Sciences

Interspecific Competition

Gary G. Mittelbach Michigan State University

Predator-prey interactions

Chapter 2. Studies in Protozoan Population Ecology

FW662 Lecture 11 Competition 1

BIOS 5970: Plant-Herbivore Interactions Dr. Stephen Malcolm, Department of Biological Sciences

The rate of prey consumption by an. The nature of predation: prey dependent, ratio dependent or neither? PERSPECTIVES

Dynamical Analysis of a Harvested Predator-prey. Model with Ratio-dependent Response Function. and Prey Refuge

A NUMERICAL STUDY ON PREDATOR PREY MODEL

Predator-Prey Population Dynamics

BIOS 6150: Ecology Dr. Stephen Malcolm, Department of Biological Sciences

Populations. ! Population: a group of organisms of the same species that are living within a certain area

Individual base model of predator-prey system shows predator dominant dynamics

The stability of ecosystems: a brief overview of the paradox of enrichment

Aggregations on larger scales. Metapopulation. Definition: A group of interconnected subpopulations Sources and Sinks

Predation. Vine snake eating a young iguana, Panama. Vertebrate predators: lions and jaguars

The Moose on Isle. An island in Lake Superior. Original migration. Another case study of the environment and environmentalists

Pangasius, a fresh water catfish with two barbels.

Deterministic extinction effect of parasites on host populations

AN EXTENDED ROSENZWEIG-MACARTHUR MODEL OF A TRITROPHIC FOOD CHAIN. Nicole Rocco

Dynamical Systems and Chaos Part II: Biology Applications. Lecture 6: Population dynamics. Ilya Potapov Mathematics Department, TUT Room TD325

BIOS 6150: Ecology Dr. Stephen Malcolm, Department of Biological Sciences

REVISION: POPULATION ECOLOGY 18 SEPTEMBER 2013

Lesson 9: Predator-Prey and ode45

Ecology - Defined. Introduction. scientific study. interaction of plants and animals and their interrelationships with the physical environment

Predator-Prey Population Models

Evidence for Competition

A Producer-Consumer Model With Stoichiometry

Rich dynamics of a ratio-dependent one-prey two-predators model

ESAIM: M2AN Modélisation Mathématique et Analyse Numérique M2AN, Vol. 37, N o 2, 2003, pp DOI: /m2an:

Introduction to population dynamics & adaptation

Prey-Predator Model with a Nonlocal Bistable Dynamics of Prey. Received: 5 February 2018; Accepted: 5 March 2018; Published: 8 March 2018

BIOS 3010: ECOLOGY. Dr Stephen Malcolm. Laboratory 6: Lotka-Volterra, the logistic. equation & Isle Royale

MA 138: Calculus II for the Life Sciences

Chapter 2 Lecture. Density dependent growth and intraspecific competition ~ The Good, The Bad and The Ugly. Spring 2013

BIO S380T Page 1 Summer 2005: Exam 2

Physics: spring-mass system, planet motion, pendulum. Biology: ecology problem, neural conduction, epidemics

Generalization in prediction of predator-prey. populations modelled by perturbed ODEs

7. E C. 5 B. 1 D E V E L O P A N D U S E M O D E L S T O E X P L A I N H O W O R G A N I S M S I N T E R A C T I N A C O M P E T I T I V E O R M U T

Interspecific Patterns. Interference vs. exploitative

Dynamics Analysis of Anti-predator Model on Intermediate Predator With Ratio Dependent Functional Responses

Unpalatable prey resolves the paradox of enrichment

The properties of a stochastic model for the predator-prey type of interaction between two species

Multiple choice 2 pts each): x 2 = 18) Essay (pre-prepared) / 15 points. 19) Short Answer: / 2 points. 20) Short Answer / 5 points

Symbology from set theory applied to ecological systems: Gause s exclusion principle and applications

It has become increasingly evident that nonlinear phenomena

Modeling and Simulation Study of Mutuality Interactions with Type II functional Response and Harvesting

Reproduction leads to growth in the number of interacting, interbreeding organisms of one species in a contiguous area--these form a population.

Lecture 5: Modelling Population Dynamics N(t)

The Effects of Varying Parameter Values and Heterogeneity in an Individual-Based Model of Predator-Prey Interaction

Answer Key Niche and Carrying Capacity Review Questions 1. A 2. A 3. B 4. A 5. B 6. A 7. D 8. C 9. A 10. B 11. A 12. D 13. B 14. D 15.

INTERPRETING POPULATION DYNAMICS GRAPH

ON THE INTERPLAY OF PREDATOR SWITCHING AND PREY EVASION IN DETERMINING THE STABILITY OF PREDATOR PREY DYNAMICS

Lab 5: Nonlinear Systems

EECS 700: Exam # 1 Tuesday, October 21, 2014

Optimal foraging and predator prey dynamics III

Critical and oscillatory behavior of a system of smart preys and predators

Impacts of radiation exposure on the experimental microbial ecosystem : a particle based model simuration approach

MATH3203 Lecture 1 Mathematical Modelling and ODEs

PREDATOR-PREY DYNAMICS

(16 µm). Then transferred to a 250 ml flask with culture medium without nitrate, and left in

Spring /30/2013

STABILITY OF EIGENVALUES FOR PREDATOR- PREY RELATIONSHIPS

Transcription:

Gause, Luckinbill, Veilleux, and What to Do Christopher X Jon Jensen Stony Brook University

Alternative Models of Predation: Functional Responses: f (N) Prey Dependent f (N/P) Ratio Dependent

Possible Outcomes of a Predator-Prey System: 1) Complete consumption of prey followed by starvation of the predator ( Dual Extinction ). 2) Oscillatory or non-oscillatory coexistence of predator and prey ( Coexistence ) 3) Starvation of the predator followed by escape of the prey ( Predator Extinction ).

The Paramecium-Didinium system: Paramecium caudatum Didinium nasutum Meets major assumptions of simple predator-prey models: Closed system Can be maintained without heterogeneities/refugia Single prey/single obligate predator Prey food can be delivered as semi-continuous input

Gause 1934: Expected: Lotka-Volterra theory predicted that all predator-prey systems should cycle indefinitely Actual: Gause found that he could not prevent his predators from completely consuming the prey population

Luckinbill 1973: Coexistence can be produced under two conditions: 1. Reduced interaction between predator and prey 2. Reduced prey food availability

Veilleux 1979: Parameter Changes High r Low r high a low a high e low e Food Concentration Number of Runs System Outcome 1.80 17 Dual Extinction 1.58 9 1.35 18 Predator Extinction 0.68 to 1.13 50 Coexistence 0.18 to 0.45 20 Predator Extinction Dual Extinction (6x) and Predator Extinction (3x) Qualitative outcome can be changed through modifications of prey food concentration

What about fitting? Prey-Dependence: better approximates Luckinbill 1973 data Ratio-Dependence: better approximates Veilleux 1979 data Despite their structural difference, the two models can produce very similar temporal dynamics both models fit very well to the data created by the other model. A good fit alone is therefore a poor indicator whether the used model correctly describes the processes that generated the data. (Jost 1998, Jost and Ellner 2000, Jost and Arditi 2001)

What about fitting? Given that in real life there would be substantial variation around the respective functions, because of stochastic environmental effects, population censusing errors, and variation in parameters among different ecosystems, we submit that the subtle difference in predictions of the prey- versus ratio-dependent models is minor and would not be detectable using simple regression tests (Lundberg and Fryxell 1995)

Possible Outcomes of a Predator-Prey System: 1) Dual Extinction 2) Coexistence 3) Predator Extinction

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change no change* CoEx DE

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change no change* CoEx DE

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change no change* CoEx DE

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change no change* CoEx DE

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change DE CoEx* CoEx DE

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change DE CoEx* CoEx DE

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) K (carrying capacity) r (prey growth rate) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx no change DE CoEx* CoEx DE

Proportional removal of prey will decrease r & K without changing other parameters: dn/dt = r0n (1 N/K) pn rp = (r0 p) Kp = K(1 p/r0)

Comparison of prey- vs. ratio dependent outcomes: Change in Parameter a (searching efficiency) Increasing levels of enforced proportional mortality (p) d (pred. death rate) e (conversion eff.) h (handling time) Prey-Dependent Outcome Ratio-Dependent Outcome DE PE; or DE CoEx CoEx DE

Experiment: PoE in reverse HP = increasing p (i.e. reducing K) in a stable system should maintain stability. [prey-dependent prediction] HR = increasing p (i.e. reducing r) in a stable system should destabilize the system. [ratio-dependent prediction]

Experiment: PoE forward HR = decreasing p (i.e. increasing r) in a stable system should maintain stability. [ratio-dependent prediction] HP = decreasing p (i.e. increasing K) in a stable system should destabilize the system. [prey-dependent prediction]

Acknowledgements: All of the thoughts presented are the result of extensive collaboration with Lev Ginzburg I am fortunate to be supported by a National Science Foundation Graduate Research Fellowship and the L.B. Slobodkin Endowment Fund for Graduate Research. http://science.czieje.com science@czieje.com

Experiment: PoE in reverse 1. 2. 3. 4. Using manipulations of methyl cellulose and prey nutrient input, find conditions under which long-term coexistence occurs Impose proportional mortality of prey in as continuous a manner as possible Continue to increase proportional mortality until dual extinction can be achieved If dual extinction occurs, use a prey-only system with the same conditions to determine if the proportional mortality level at which dual extinction occurs corresponds to r < 0 or r >0

Experiment: PoE forward 1. 2. 3. 4. 5. Begin with a system where high proportional mortality is being enforced Using manipulations of methyl cellulose and prey nutrient input, find conditions under which long-term coexistence occurs Increase r by incrementally releasing the system from enforced proportional mortality Continue to decrease proportional mortality until dual extinction can be achieved Note the problem here with having to prove the absence of a phenomenon

Luckinbill 1973: Dual Extinction

Luckinbill 1973: Predator Extinction

Luckinbill 1973: Coexistence