SOME ELEMENTARY MECHANISMS FOR CRITICAL TRANSITIONS AND HYSTERESIS IN SIMPLE PREDATOR PREY MODELS. John Vandermeer i. Abstract

Similar documents
It has become increasingly evident that nonlinear phenomena

The Dynamic Behaviour of the Competing Species with Linear and Holling Type II Functional Responses by the Second Competitor

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

Spatial pattern and power function deviation in a cellular automata model of an ant population

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

Gary G. Mittelbach Michigan State University

Ecology 302: Lecture VII. Species Interactions.

3.5 Competition Models: Principle of Competitive Exclusion

Turing and Non-Turing patterns in diffusive plankton model

Wada basins and qualitative unpredictability in ecological models: a graphical interpretation

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

Stability of Ecosystem Induced by Mutual Interference between Predators

Math 232, Final Test, 20 March 2007

Lab 5: Nonlinear Systems

Early warning signs in social-ecological networks

A NUMERICAL STUDY ON PREDATOR PREY MODEL

Interspecific Competition

8 Ecosystem stability

BIOL 410 Population and Community Ecology. Predation

Introduction to Dynamical Systems Basic Concepts of Dynamics

Ecology Regulation, Fluctuations and Metapopulations

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

Basins of Attraction and Perturbed Numerical Solutions using Euler s Method

Models Involving Interactions between Predator and Prey Populations

Populations Study Guide (KEY) All the members of a species living in the same place at the same time.

Local Stability Analysis of a Mathematical Model of the Interaction of Two Populations of Differential Equations (Host-Parasitoid)

Mathematical Biology - Lecture 1 - general formulation

Stability, dispersal and ecological networks. François Massol

Lecture 20/Lab 21: Systems of Nonlinear ODEs

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

Antagonistic and Synergistic Interactions Among Predators

A Producer-Consumer Model With Stoichiometry

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

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

Workshop on Theoretical Ecology and Global Change March 2009

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

Species interaction in a toy ecosystem

Key words and phrases. Bifurcation, Difference Equations, Fixed Points, Predator - Prey System, Stability.

Lecture 3. Dynamical Systems in Continuous Time

The logistic difference equation and the route to chaotic behaviour

Numerical Solution of a Fractional-Order Predator-Prey Model with Prey Refuge and Additional Food for Predator

Adaptive Traits. Natural selection results in evolution of adaptations. Adaptation: trait that enhances an organism's survival and reproduction

Stability Analysis of a Continuous Model of Mutualism with Delay Dynamics

Chaos and adaptive control in two prey, one predator system with nonlinear feedback

COMPETITION OF FAST AND SLOW MOVERS FOR RENEWABLE AND DIFFUSIVE RESOURCE

Parameter Sensitivity In A Lattice Ecosystem With Intraguild Predation

ROLE OF TIME-DELAY IN AN ECOTOXICOLOGICAL PROBLEM

Introduction to Biomathematics. Problem sheet

Resilience and stability of ecological networks. Elisa Thébault

2 One-dimensional models in discrete time

MA 138 Calculus 2 for the Life Sciences Spring 2016 Final Exam May 4, Exam Scores. Question Score Total

ARTICLE IN PRESS. Journal of Theoretical Biology

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

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

8. Qualitative analysis of autonomous equations on the line/population dynamics models, phase line, and stability of equilibrium points (corresponds

Predator-Prey Model with Ratio-dependent Food

Continuous Threshold Policy Harvesting in Predator-Prey Models

Global dynamics of a mutualism competition model with one resource and multiple consumers

SARAH P. OTTO and TROY DAY

NONSTANDARD NUMERICAL METHODS FOR A CLASS OF PREDATOR-PREY MODELS WITH PREDATOR INTERFERENCE

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

Behaviour of simple population models under ecological processes

Dynamical Systems: Ecological Modeling

Computing 3D Bifurcation Diagrams

4. Ecology and Population Biology

LIMIT CYCLE OSCILLATORS

JOURNAL OF MATH SCIENCES -JMS- Url: Jl. Pemuda, No. 339 Kolaka Southeast Sulawesi, Indonesia

A Primer of Ecology. Sinauer Associates, Inc. Publishers Sunderland, Massachusetts

SEMELPAROUS PERIODICAL INSECTS

An Application of Perturbation Methods in Evolutionary Ecology

A Stability Analysis on Models of Cooperative and Competitive Species

Global Stability Analysis on a Predator-Prey Model with Omnivores

Multiple stable points, tipping points, and warning signs in ecological systems

HARVESTING IN A TWO-PREY ONE-PREDATOR FISHERY: A BIOECONOMIC MODEL

Analyzing the Parameters of Prey-Predator Models for Simulation Games

Introduction to Dynamical Systems

Math 1280 Notes 4 Last section revised, 1/31, 9:30 pm.

The Effect of a Rotational Spring on the Global Stability Aspects of the Classical von Mises Model under Step Loading

Optimal foraging and predator prey dynamics III

Dynamics of Disease Spread. in a Predator-Prey System

Gerardo Zavala. Math 388. Predator-Prey Models

Discrete Time Coupled Logistic Equations with Symmetric Dispersal

Population Ecology and the Distribution of Organisms. Essential Knowledge Objectives 2.D.1 (a-c), 4.A.5 (c), 4.A.6 (e)

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

Hydra Effects in Stable Communities and Their Implications for System Dynamics

Ordinary Differential Equations

2D-Volterra-Lotka Modeling For 2 Species

Student Background Readings for Bug Dynamics: The Logistic Map

Complex Systems Theory and Evolution

The relationships between cannibalism and pattern formation in spatially extended preypredator

Analyzing the Parameters of Prey-Predator Models for Simulation Games

Model Stability Analysis of Marine Ecosystem

Understanding Populations Section 1. Chapter 8 Understanding Populations Section1, How Populations Change in Size DAY ONE

Numerical Algorithms as Dynamical Systems

Ecology. Bio Sphere. Feeding Relationships

A Note on the Ramsey Growth Model with the von Bertalanffy Population Law

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

x 2 F 1 = 0 K 2 v 2 E 1 E 2 F 2 = 0 v 1 K 1 x 1

Global analysis of the nonlinear Duffing-van der Pol type equation by a bifurcation theory and complete bifurcation groups method

Chapter 6 Reading Questions

Transcription:

SOME ELEMENTARY MECHANISMS FOR CRITICAL TRANSITIONS AND HYSTERESIS IN SIMPLE PREDATOR PREY MODELS John Vandermeer i Abstract Trait-mediated indirect effects are increasingly acknowledged as important components in the dynamics of ecological systems. The hamiltonian form of the LV equations is traditionally modified by adding density dependence to the prey variable and functional response to the predator variable. Enriching these non-linear elements with a trait-mediation added to the carrying capacity of the prey creates the dynamics of critical transitions and hysteretic zones. The fundamental predator prey models of Lota and Voltera (LV), have long formed the foundation of much of theoretical ecology (Vandermeer and Goldberg, 2013). Other approaches, such as matrix projections (Caswell, 2001 ), interative maps (May, 1980), stochastic processes (Chesson, 1991), reaction-difussion equations (Levin, 1979) have also been important, but the LV approach continues to motivate the development of much theory (Vandermeer, 2004). Independently, the recognition of hysteresis and critical transitions has more recently become an important theme in ecology (Sheffer, 2009), with a major focus on empirical applications (Sheffer et al., 2012). In this note I elaborate some elementary extensions of the basic 2D LV approach in which known ecological factors create background conditions that may lead to hysteresis and critical transitions. Consider the following two dimensional system: dt = B &(C, R)C M & (C, R)C dt = B -(C, R)R M - (C, R)R 1 where C is the predator (consumer) and R is the prey (resource), Bi is the birth rate and Mi is the mortality rate. If we allow B1 to be a simple linear function of R and M2 a simple linear function of C, and M1 and B2 constant, we have: dt = arc mc 2 dt = br arc which is to say, the classic quasi-hamiltonian form of the LV equations. In elementary ecological considerations it is common to begin with the R having a logistic form, when C=0, whence, i Department of Ecology and Evolutionary Biology, University of Michigan, Ann Arbor, MI 48109. jvander@umich.edu 1

and thus B - M - = r(1 R K ) 45 46 = rr 7 8 R2 3 It is evident that as R--> 0, d(lnr)/dt --> r, and for any R > 0, d(lnr)/dt < r by a factor of r/k. In ecology the two parameters r and K are referred to as the intrinsic rate of natural increase (herein, the intrinsic rate), and the carrying capacity, respectively. Herein we refer to r/k as the discount rate, for obvious reasons. Formulating M2 as in equation 2, equation 3 expands to, 45 46 = rr 7 8 R2 arc = R(r arc) 7 8 R2 4 whence it is evident that this classic form effectively assumes that the predator acting on the system is introduced through the intrinsic rate. There is, of course, no reason why the predator could not operate through the discount rate instead (or in addition to). For example, if the presence of the predator induces the prey to find more places to hide, or stimulates it to seek food at a higher rate, the introduction of the predator into the system can be taken as acting through the discount rate. Ecologically speaking we can formulate this obvious factor by making the carrying capacity an increasing function of the predator, and equation 4 becomes, 45 46 = R(r arc) 7 8 ; <=> R2 5 Equation 5 represents two effects of the predator, one "direct" effect (parameter a) and one "indirect" effect (parameter k, which we assume is positive -- a negative k does not give interesting results and will not be discussed). The indirect effect here is almost certainly a result of some modification of a "trait" of the prey (e.g. the ability to locate predator-free space) and is thus, in the current terminology popular in ecology, a "trait-mediated indirect effect" (effectively equivalent to the older usage of "higher order effect"). A concrete example is the classical ant/hemipteran mutualism (Zhang et al., 2012) wherein the ant is ultimately a predator of the hemipteran (either directly by consuming, or indirectly by extracting energy from the honeydew secreted by the hemipterans), yet allows the hemipterans to build up very large populations by protecting them from other, more devastating, natural enemies such as parasitic or predatory insects. Thus, this trait-mediated effect changes equation set 2 and we arrive at: dt = rr(1 dt = arc mc 6 R K? + kc ) arc The zero growth isoclines of system 6 are: 2

R = m a ` 7 R = K? + ( k a r K?)C ak r C- whence it is evident that various parameters taken as tuning parameters can produce both critical transition behavior and hysteresis. The phase plane with isoclines and vector field along with a few trajectories is illustrated in figure 1a. Since the predator isocline is R = m/a, using m as the tuning parameter, the visualization is a decreasing intercept (on the R axis) of the predator isocline. Such changes (illustrated in fig 1a) clearly result in a pattern of critical transitions embracing a zone of hysteresis (Fig 1b). Figure 1. a. The isoclines, vector field, and illustrative trajectories (equation set 7) of the basic model (equations 6) using m as a tuning parameter. Predator isocline (vertical lines) shown for a = 1.2, 1.003, 0.95, 0.8, and 0.6 respectively from right to left. Clearly the hysteretic zone is between a=1.003 and 0.7, with a saddle/node bifurcation at a=1.003, a stable focus as the upper equilibrium and prey=1 (its carrying capacity) and predator = 0 the lower equilibrium. (Other parameters are, K0 = 1; k = 6, r=0.4). b. Critical transition graph for a. Independently of any consideration of critical transitions or hysteresis, Noy Meir (1975) elaborated a graphical approach to the LV model that effectively added three nonlinear components to the basic model. In particular, the prey population was thought to be density dependent (i.e., a carrying capacity was added for the prey), the predator was thought to have a functional response (i.e., at high levels of prey, the predator becomes saturated) and the predator was thought to be dependent on its own density (i.e., some other factor in the environment, other than the prey, limited the predator population at high densities). Following Ong and Vandermeer (2018), with M2 = m, we have, 3

B - = r & (1 R K 5 ) and additionally, B & = r -R 1 + br (1 C K > ) M - = ac 1 + br whence equation set 1 becomes with zero growth isoclines, dt = r -R 1 + br (1 C )C mc K > dt = r &R(1 R ) arc K 5 1 + br 8 C = K > mk >(1 + br) Rr - 9 illustrated in figure 2. C = r & a B1 R K 5 C (1 + br) 4

Figure 2. Exemplary graphic displays of equations 9 (in phase space with zero growth isoclines and vector fields, for various parameter values). In a, b and c, the dashed red curve indicates an unstable inset to the saddle point. In e and f the dashed black curve indicates stable limit cycle. a. parameters r2 = 2; b = 5; KC = 1.4; m = 0.1; r1 = 3.3; KR = 3; a = 8. b. parameters same as in a except KC = 2. c. parameters same as in a except KC = 0.8; m = 0.2; r1 = 1.28; KR = 2; d. parameters same as in a except r2 = 3; KC = 0.8; m = 0.2; r1 = 1.28; KR = 0.3; e. parameters same as in a except r2 = 3; KC = 0.8; m=0.2; r1 = 1.28; KR = 1. f. Stable limit cycle repeatedly approaching R = 0, effectively driving R extinct, which is followed by C going extinct also. Parameters same as in a except KC = 2.72. If the conditions giving rise to equations 8 are expanded to include the trait mediated conditions of equations 6, the following equations arise: dt = r -R 1 + br (1 C )C mc K > dt = r &R(1 R (K 5 + kc) ) arc 1 + br 10 with zero growth isoclines, C = K > mk >(1 + br) Rr - 11 C(K 5 r &k a ) + kc- = r & a K 5 + B r &bk 5 r & a a C R r &b a R- + r &kb a RC The resulting qualitative dynamics are illustrated in figure 3. There are obviously two distinct regions of hysteresis (fig 3a and c), qualitatively corresponding to the previous hysteretic patterns (equations 6 and 9), not surprisingly since equations 10 are a combination of the two mechanisms. Note that the sketch in figure 3d is approximate since it is a consensus of bifurcation diagrams with various values of C0 (the initiation values of C). Properly it should be displayed in 3D, but the basic qualitative nature of the diagram does not change, and it is evident from the dashed red lines (representing the separatrices of the two basins) in figs 3a and c, that the initial value of C will make a difference in the details, but the basic structure of the critical transition graph in figure 3d, will not change much. It is worth noting that the hysteretic patterns suggested in figure 3 occur at distinct points along the range of predator mortality and carrying capacity values (m), similar to that reported elsewhere (Ong and Vandermeer, 2018). With more complicated tuning parameters such hysteretic zones can overlap. 5

In summary, the basic idea of a trait-mediated indirect interaction can be incorporated as a "higher order interaction" in a variety of ways. Here we explore the consequences of a framework in which the parameter corresponding to the carrying capacity of the prey species is augmented by the presence of a predator. This framing adds a nonlinear component as a divisor of one of the terms, resulting in some complicated oscillatory behavior in the basic model. The existence of critical transitions bordering hysteritic zones emerges with both trait-mediated additions and a classic functional response to the predator. Incorporating functional response along with trait mediation interestingly may result in a dual hysteretic zone, paralleling the zones that emerge from each of those nonlinearities added separately. Figure 3. a,b, and c: Exemplary graphic displays of equations 11 (in phase space with zero growth isoclines and vector fields, for various values of the parameter m). d. Sketch of maximum and minimum resource values at different values of m, where the carrying capacity of the predator is given as 15.8m - 6.73, assuming that there is a tradeoff between mortality and carrying capacity. It is worth noting that the hysteretic patterns suggested in figure 3 occur at distinct points along the range of predator mortality and carrying capacity values (m), similar to that reported elsewhere (Ong and Vandermeer, 2018). With more complicated tuning parameters such hysteretic zones can overlap. 6

References Caswell, H. (2001). Matrix population models. John Wiley & Sons, Ltd. Chesson, P. (1991). Stochastic population models. In Ecological heterogeneity (pp. 123-143). Springer, New York, NY. Levin, S. A. (1979). Non-uniform stable solutions to reaction-diffusion equations: applications to ecological pattern formation. In Pattern formation by dynamic systems and pattern recognition (pp. 210-222). Springer, Berlin, Heidelberg. May, R. M. (1980). Nonlinear phenomena in ecology and epidemiology. Annals of the New York Academy of Sciences, 357(1), 267-281. Noy-Meir, I. (1975). Stability of grazing systems: an application of predator-prey graphs. The Journal of Ecology, 459-481. Ong, T., and Vandermeer, J. 2018. Multiple Hysteretic Patterns from Elementary Population Models. Theoretical Ecology, in press. Scheffer, M. (2009). Critical transitions in nature and society. Princeton University Press. Scheffer, M., Carpenter, S.R., Lenton, T.M., Bascompte, J., Brock, W., Dakos, V., Van de Koppel, J., Van de Leemput, I.A., Levin, S.A., Van Nes, E.H., Pascual, M., and Vandermeer, J. (2012). Anticipating critical transitions. science, 338(6105), pp.344-348. Vandermeer, J. (2004). Coupled oscillations in food webs: balancing competition and mutualism in simple ecological models. The American Naturalist, 163(6), 857-867. Vandermeer, J. H., & Goldberg, D. E. (2013). Population ecology: first principles. Princeton University Press. Zhang, S., Zhang, Y., & Ma, K. (2012). The ecological effects of the ant hemipteran mutualism: a meta-analysis. Basic and Applied Ecology, 13(2), 116-124. 7