Chaotic Dynamics Can Select for Long-Term Dormancy *

Similar documents
The effect of emigration and immigration on the dynamics of a discrete-generation population

2 One-dimensional models in discrete time

Behaviour of simple population models under ecological processes

Natal versus breeding dispersal: Evolution in a model system

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

Parameter Sensitivity In A Lattice Ecosystem With Intraguild Predation

Asynchronous and Synchronous Dispersals in Spatially Discrete Population Models

Scale-free extinction dynamics in spatially structured host parasitoid systems

Math 345 Intro to Math Biology Lecture 7: Models of System of Nonlinear Difference Equations

Stability Analyses of the 50/50 Sex Ratio Using Lattice Simulation

Life history evolution

Genetic Variability in Sensitivity to Population Density Affects the Dynamics of Simple Ecological Models

Evolutionary Predictions from Invariant Physical Measures of Dynamic Processes

Chapter 9 Population Dynamics, Carrying Capacity, and Conservation Biology

How to Use This Presentation

Current controversies in Marine Ecology with an emphasis on Coral reef systems

Ecology Regulation, Fluctuations and Metapopulations

Module BIO- M1- S06 Evolu-onary ecology. Adaptive dynamics. David Claessen Ins-tut de Biologie de l ENS Equipe Eco- Evolu-on Mathéma-que

Current controversies in Marine Ecology with an emphasis on Coral reef systems. Niche Diversification Hypothesis Assumptions:

Stabilization through spatial pattern formation in metapopulations with long-range dispersal

A Simulation of the Process of Evolution Modified from Biology Labs On-Line (Pearson)

Stability Of Specialists Feeding On A Generalist

Introduction to course: BSCI 462 of BIOL 708 R

Major questions of evolutionary genetics. Experimental tools of evolutionary genetics. Theoretical population genetics.

Evolutionary quantitative genetics and one-locus population genetics

The struggle for existence

The upper limit for the exponent of Taylor s power law is a consequence of deterministic population growth

Maintenance of Species Diversity by Predation in the Tierra System

Kalle Parvinen. Department of Mathematics FIN University of Turku, Finland

On Evolutionary Stability in Predator-Prey Models with Fast Behavioral Dynamics

EVOLUTION OF LEARNING IN FLUCTUATING ENVIRONMENTS: WHEN SELECTION FAVORS BOTH SOCIAL AND EXPLORATORY INDIVIDUAL LEARNING

BIOS 3010: Ecology Lecture 14: Life Histories: 2. Components of life histories: Growth, fecundity and survivorship. 3. Components of life histories:

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

Contents PART 1. 1 Speciation, Adaptive Radiation, and Evolution 3. 2 Daphne Finches: A Question of Size Heritable Variation 41

Homework 2 Modeling complex systems, Stability analysis, Discrete-time dynamical systems, Deterministic chaos

DARWIN: WHICH MATHEMATICS?

THE EVOLUTION OF INTERTEMPORAL PREFERENCES

Case Studies in Ecology and Evolution

Complex networks and evolutionary games

Summary. A Bird s- Eye View of Community and Population Effects of Ontogenetic Development

Gibbs: The Investigation of Competition

Temperature. (1) directly controls metabolic rates of ectotherms (invertebrates, fish) Individual species

To appear in the American Naturalist

COMPARING ENVIRONMENTAL AND GENETIC VARIANCE AS ADAPTIVE RESPONSE TO FLUCTUATING SELECTION

Adaptation. Biotic and Abiotic Environments. Eric R. Pianka

Chapter 6 Reading Questions

Population Ecology. Chapter 44

Chapter 2 Section 1 discussed the effect of the environment on the phenotype of individuals light, population ratio, type of soil, temperature )

Environmental Variation, Stochastic Extinction, and Competitive Coexistence

A simple genetic model with non-equilibrium dynamics

Chapter 8. Biogeographic Processes. Upon completion of this chapter the student will be able to:

The Wright-Fisher Model and Genetic Drift

CH 16: Evolution of Population

population size at time t, then in continuous time this assumption translates into the equation for exponential growth dn dt = rn N(0)

Gary G. Mittelbach Michigan State University

Introduction to Evolution

History and meaning of the word Ecology A. Definition 1. Oikos, ology - the study of the house - the place we live

Selection for late pupariation affects diapause incidence and duration in the flesh fly, Sarcophaga bullata

The concept of adaptive phenotypic polymorphism in evolutionary theory

A population is a group of individuals of the same species occupying a particular area at the same time

Levels of Ecological Organization. Biotic and Abiotic Factors. Studying Ecology. Chapter 4 Population Ecology

Chapter 4 Population Ecology

Introduction to population dynamics & adaptation

Evolving plastic responses to external and genetic environments

REVIEW 6: EVOLUTION. 1. Define evolution: Was not the first to think of evolution, but he did figure out how it works (mostly).

Lecture 2: Individual-based Modelling

The Limiting Similarity, Convergence, and Divergence of Coexisting Species

Chapter 6 Population and Community Ecology

It has become increasingly evident that nonlinear phenomena

EVOLUTION change in populations over time

Chapter 8: Evolution and Natural Selection

Metacommunities Spatial Ecology of Communities

Population Ecology Density dependence, regulation and the Allee effect

Computer Simulations on Evolution BiologyLabs On-line. Laboratory 1 for Section B. Laboratory 2 for Section A

Notes and Comments. Variation in and Correlation between Intrinsic Rate of Increase and Carrying Capacity. Nora Underwood *

Principles of Ecology BL / ENVS 402 Exam II Name:

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

Evolutionary Dynamics of Seed Size and Seedling Competitive Ability

(Write your name on every page. One point will be deducted for every page without your name!)

IV. Natural Selection

PREDATOR AND PREY HABITAT SELECTION GAMES: THE EFFECTS OF HOW PREY BALANCE FORAGING AND PREDATION RISK

PULSE-SEASONAL HARVESTING VIA NONLINEAR DELAY DIFFERENTIAL EQUATIONS AND APPLICATIONS IN FISHERY MANAGEMENT. Lev V. Idels

EVOLUTION change in populations over time

A DISCRETE-TIME HOST-PARASITOID MODEL

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

Evolutionary-branching lines and areas in bivariate trait spaces

EVOLUTION. HISTORY: Ideas that shaped the current evolutionary theory. Evolution change in populations over time.

The logistic difference equation and the route to chaotic behaviour

Sexual Reproduction. Page by: OpenStax

Lecture 8 Insect ecology and balance of life

BIOL 410 Population and Community Ecology. Density-dependent growth 2

3.5 Competition Models: Principle of Competitive Exclusion

Antagonistic and Synergistic Interactions Among Predators

Long-term adaptive diversity in Levene-type models

Spontaneous pattern formation and genetic invasion in locally mating and competing populations

The evolution of dispersal and seed size in plant communities

Evolutionary Branching and Sympatric Speciation Caused by Different Types of Ecological Interactions

5/31/2012. Speciation and macroevolution - Chapter

The implications of neutral evolution for neutral ecology. Daniel Lawson Bioinformatics and Statistics Scotland Macaulay Institute, Aberdeen

Application of Cellular Automata in Conservation Biology and Environmental Management 1

Transcription:

vol. 168, no. 1 the american naturalist july 2006 Chaotic Dynamics Can Select for Long-Term Dormancy * R. G. Lalonde 1,2, and B. D. Roitberg 2, 1. Unit of Biology and Physical Geography, University of British Columbia Okanagan, 3333 University Way, Kelowna, British Columbia V1V 1V7, Canada; 2. Behavioural Ecology Research Group, Department of Biological Sciences, Simon Fraser University, Burnaby, British Columbia V5A 1S6, Canada Submitted May 20, 2005; Accepted March 29, 2006; Electronically published May 11, 2006 abstract: Extended dormancy in a population is evolutionarily costly unless some variance in season-to-season fitness (usually driven by variance in environmental quality) makes bet hedging useful. Consequently, dormancy in a population is usually accepted as evidence of environmental variance. Using a Ricker-type model with heritable variation in dormancy, we show that this need not be so. Intrinsic population dynamics can generate chaotic fluctuations in the absence of environmental variance. Chaotic dynamics increase the frequency of a range of dormant strategists under natural selection, even when mortality during dormancy is relatively high. The buffering effect of dormant individuals then eliminates chaotic dynamics or generates periodic orbits of relatively low amplitude. These stabilized populations harbor a high frequency of dormant individuals that express a range of propensities to enter dormancy. Keywords: chaos, diapause, dormancy, risk spreading, demographic, bet hedging. Paradoxes are common in biology. For example, many organisms, such as plants and insects, commonly exhibit long-distance dispersal or dormancy extending for many generations (Hanski 1988). Such strategies are problematic because direct fecundity costs associated with dispersal and the demographic costs incurred by delaying reproduction result in reduction of fitness. Although dispersal and dormancy allow organisms to hedge against highly variable environments (Denno et al. 1991; Holt and McPeek 1996) or temporally variable mortality resulting from predation * The authors contributed equally to this work. E-mail: robert.lalonde@ubc.ca. E-mail: bernard_roitberg@sfu.ca. Am. Nat. 2006. Vol. 168, pp. 127 131. 2006 by The University of Chicago. 0003-0147/2006/16801-41089$15.00. All rights reserved. (Ringel et al. 1998), these tactics can also persist in situations where no variance source is apparent (Denno et al. 1991; Aluja et al. 1998). When the latter is true, it is usual to assume selection from some unmeasured environmental variance-driving factor (Danks 1992; Hopper 1999). A second paradox is that internally generated chaotic dynamics are a feature of many ecological models (Hassell et al. 1976; May 1976), but such dynamics have rarely been demonstrated in nature (Hassell et al. 1976; Turchin and Ellner 2000). It is usual to ascribe this absence of evidence to the difficulties associated with separating the effects of intrinsic and extrinsic factors on population dynamics (Turchin and Ellner 2000). We describe here a scenario where natural selection in chaotic populations favors the spread of a demographically costly risk-spreading strategy. In this case, we model dormancy evolution, but our results are broadly applicable to dispersal as well. Although it is well known that dormant (or dispersing) individuals can stabilize population dynamics (Bulmer 1984; Van Dooren and Metz 1998; Newman et al. 2002), it is not known whether dormancy can evolve in a chaotic population, given its demographic cost. We demonstrate here that allowing natural selection for dormancy generates very stable dynamics in otherwise chaotic systems while maintaining a high frequency of dormant strategists. The Model We begin with a population constrained to a single strategy of nondormancy whose dynamics are described by the familiar Ricker (1954) equation (using the discrete-time logistic produces identical qualitative results; May 1976), N p RN e t t 1 t, (1) where the population at one time step in the future, N t 1, is a function of the replacement rate (R) and the negative influence (competition, cannibalism) of the present population ( t ). This model has the useful characteristic of displaying dynamics that range from extreme stability at low values of R to a series of period-doubling bifurcations leading to chaos as R increases (fig. 1). We modify this basic model to include dormancy, where

128 The American Naturalist One convenient aspect of this approach is that it allowed us to assign dormancy fates directly to individuals such that the duration of each individual s term of dormancy was defined at birth to be of a specific duration. This avoids problems associated with simply assigning Markov probabilities to the processes of entering and leaving the dormant pool. The latter approach makes for analytically tractable models. However, in numerical models, this practice has the effect of creating individuals that can experience very long dormancies because the likelihood that any individual in the dormant pool will ultimately break dormancy is independent of the length of time that the individual has been dormant. Figure 1: Ricker population dynamics. Bifurcation plot shows the effect of changing the replacement rate (R) on population stability in Rickertype populations with no dormancy. a parent s offspring show a range of dormancies with a mean that we allowed to range from zero to five generations. Actual dormancies across individuals are assigned according to a Poisson distribution, to a maximum of 13 generations of dormancy, with the very small fraction of dormancies that would have been assigned values greater than the maximum set to that maximum value. The population of active individuals at time t 1, N t 1, is now given by [ t t 1 t 0j ] 1 t jp0 N p RN e (p ) d (1 m). (2) Here, p 0j is the proportion of the population that is composed of individuals of genotype j that express no dormancy, and d 1t is the element of vector d that contains the number of individuals at time t that have broken dormancy at time t 1 and have escaped density-independent mortality (m). Additionally, all individuals in the dormancy vector d that survive one season of dormancy are moved to the next lowest element (e.g., d 5 to d 4 ) each generation. Finally, each element of d at time t is also updated by direct recruitment of the dormant offspring of active individuals of genotype j. Thus, [ t i t ij ] t i 1t 1 jp0 d p RN e (p ) d (1 m). (3) Sensitivity Analyses for Evolving Dormancy We started our population with no dormant strategists and allowed dormancy to appear by mutation after 1,900 generations and for the next 100 generations. To do this, we introduced a mutation rate of 0.002/individual that could result in a spontaneous change in the maternal strategy with respect to dormancy. Depending on the magnitude of the replacement rate (R), this meant that over 100 generations, anywhere from 200 to 2,000 mutants were introduced into the population. Natural populations with dormancy typically express a range of dormancy durations (Menu et al. 2000). We assume here that this variation is a genotypic strategy, and we have all mutant strategists play a mixed game wherein progeny display a range of dormancies with a genotypically specific mean value rather than a dormancy of fixed duration. For computational purposes, we discretized this range into value increments of 0.5. When a mutation occurred, the offspring of the individual with the mutation all carried the same resulting genotype (asexual inheritance). After the population was seeded with dormant strategists, mutation was terminated, and the model population was allowed to evolve for a further 3,000 generations. At the end of this time, the population size during the last 50 generations was recorded, along with the distribution of strategists within the population. All combinations of parameters were replicated 10 times. The model setup did not lend itself to classical analysis for determining evolutionary stable states. However, we did test the robustness of our results by a perturbation analysis as a complement to each of the replicate runs described above. Our results below are robust with respect to variation in the density-dependent mortality term (d) in the Ricker model. Our model produces several striking results. First, the unstable dynamics displayed by the original Ricker model essentially disappear with the invasion of dormancy. Parameter combinations that would otherwise produce a period doubling to chaos (fig. 1; Hassell et al. 1976; Newman et al. 2002) instead produce stable equilibria, simple twophase cycles, or periodic orbits of relatively narrow amplitude (fig. 2). Second, we find that populations support dormant strategists above the threshold replacement rate that would normally see the beginning of the perioddoubling process in the unmodified Ricker model. Most interestingly, we see that a range of dormancy strategies, rather than a single optimal dormancy strategy, is maintained (fig. 3). This effect is most pronounced at zero or

Chaos and Dormancy 129 Figure 2: Dynamics of Ricker systems with dormancy allowed to invade. Plots show the effect of increasing mortality (m) during dormancy on system dynamics. Active individuals (Y-axis) are those individuals in the population that are not dormant at any given time; they may be either nondormant or dormant strategists. low mortality levels and is much less evident with strong mortality during the dormant phase (fig. 3). This production of a range of dormancy strategies is robust in a qualitative way. Replicate runs produce similar but slightly different ranges of dormancy strategies under identical parameters and show a strong tendency to return to similar states after perturbation (results not shown). Finally, we find that higher replacement rates tend to increase population fluctuations, in this case manifested by the system entering periodic orbits of increasing amplitude. These orbits are driven by temporal fluctuation of strategist frequencies, in a manner similar to that of Doebeli s (1993, 1995) intermittent chaos and laboratory predator-prey systems (Yoshida et al. 2003). The first two results, system stability and invasion and maintenance of dormancy, compare very closely with findings of other studies on the evolution of demographically costly strategies. It has been amply demonstrated, at least theoretically, that dispersal and dormancy can be maintained in variable environments (e.g., Hopper 1999). For example, Menu et al. (2000) showed that a pure riskspreading strategy can, despite its demographic cost, perform very well when environmentally determined mortality varies greatly over time. Furthermore, Doebeli (1995) demonstrated that chaotic dynamics can be ameliorated by introduction of demographically costly strategies, although he did not invoke specific biological mechanisms. In a similar way, Newman et al. (2002) showed that a dormant pool can stabilize Ricker-type dynamics over a range of parameters, but they did not evaluate the fitness of dormant strategies. Finally, Holt and McPeek (1996) showed that dispersal strategies are favored under natural selection in chaotic systems, which in turn affect system dynamics. Maintenance of a range of genotypes within a model system suggests that there is no unique evolutionarily stable strategy (ESS) for many sets of parameters. This type of result can be obtained in randomly fluctuating (Sasaki and Ellner 1995) or cyclical systems where strategists differ markedly in functional response to resource availability (Armstrong and McGehee 1976; Abrams and Holt 2002). However, our model includes none of these features. Instead, we see a mixture of dormancy strategy genotypes under parameter sets that ultimately result in strong population stability once dormancy invades (fig. 2). This result may have been obtained when mortality during dormancy was set to zero because selection against increased mean time to reproduction goes to zero in equilibrium populations (Karban 1997; Van Dooren and Metz 1998). In this light, adding mortality during dormancy should have two effects. First, because mortality imposes a demographic cost on all dormant strategists, high mortality should select for the shortest dormancy duration that stabilizes system dynamics. We find exactly this. The average duration of dormancies present in the population is much more constrained when m p 0.50 than when m p 0.05, 0.005, or 0 (fig. 3). Second, the demographic cost that mortality imposes on dormancy should produce variation in strategy fitness at system equilibrium. Thus, if absence of mortality is the sole factor allowing a wide range of dormancy strategists to coexist, any mortality should select for a single optimum genotype. This does not happen. However, our results suggest that increasing mortality does force these systems to approach such a single optimum. We find that

130 The American Naturalist Figure 3: Frequency distribution at the end of simulations of dormancy genotypes as affected by replacement rate and mortality during dormancy. Distributions show the effect of varying mortality (columns) and replacement rate (rows) on the distribution of dormancy genotypes after 3,000 generations. Each run was replicated 10 times, and distributions represent the mean of all trials. Light hatched bars represent proportion of the population that is composed of nondormant genotypes. Dark stippled bars represent dormancy genotypes. Error bars denote 1 standard error. moderate to low mortalities result in a range of dormancy strategies being maintained in the population, whereas very strong mortality ( m p 0.5) produces the lowest var- iation among dormancy strategists (fig. 3). Finally, an ESS analysis of a simpler model may shed some light on whether coexistence of multiple dormancy strategies is actually a mixed ESS or represents an intermediate stage along a very slow march to a monomorphic ESS. Both Doebeli s (1995) and Holt and McPeek s (1996) models readily generated intermittent chaos that was driven by negative frequency-dependent selection. Our model never generates intermittent chaos but does generate periodicity at higher replacement rates when very long average dormancies are selected or at lower replacement rates with mortality during dormancy added to the mix. The periodicity obtained at high replacement rates in our model probably occurs because no dormancy genotype within the range allowed can fully stabilize these systems, even when there is no mortality during dormancy (fig. 2). Mortality during dormancy further destabilizes our system. This occurs because mortality increases the demographic cost of dormancy when the system is stable and thus reduces the fitness of dormant strategists. This reduces their frequency and causes system fluctuation, which in turn increases dormant strategist fitness (and thus strategist frequency). This temporal fluctuation of strategist frequency drives system oscillations that take the form of periodic orbits at low to moderate mortalities and strong two- and four-phase cycles at high mortalities. We return to the paradox. Dormancy should not exist in stable populations, and we find that this holds true here. At low replacement rates, dormancy never invades when rare and tends to disappear if added in large frequencies as a perturbation. Chaotic dynamics selects for dormancy because the bet-hedging strategy gives higher geometric mean fitness to dormant individuals than to nondormant strategists. The resultant high frequency of dormancy then eliminates the chaotic dynamics, and the system persists in a much more stable condition. Acknowledgments The Natural Sciences and Engineering Research Council of Canada provided funding to B.D.R., and Okanagan Uni-

Chaos and Dormancy 131 versity College (now University of British Columbia Okanagan) provided computer facilities for R.G.L. M. Doebeli and B. Ma kindly commented on an early draft of the manuscript. Literature Cited Abrams, P. A., and R. D. Holt. 2002. The impact of consumerresource cycles on the coexistence of competing consumers. Theoretical Population Biology 62:281 295. Aluja, M., M. López, and J. Sivinski. 1998. Ecological evidence for diapause in four native and one exotic species of larval-pupal fruit fly (Diptera: Tephritidae) parasitoids in tropical environments. Annals of the Entomological Society of America 91:821 833. Armstrong, R. A., and R. McGehee. 1976. Coexistence of two competitors on one resource. Theoretical Population Biology 56:499 502. Bulmer, M. G. 1984. Delayed germination of seeds: Cohen s model revisited. Theoretical Population Biology 26:367 377. Danks, H. V. 1992. Long life cycles in insects. Canadian Entomologist 124:167 187. Denno, R. F., G. K. Roderick, K. L. Olmstead, and H. G. Dobel. 1991. Density-related migration in planthoppers (Homoptera: Delphacidae): the role of habitat persistence. American Naturalist 138: 1513 1541. Doebeli, M. 1993. The evolutionary advantage of controlled chaos. Proceedings of the Royal Society of London B 254:281 285.. 1995. Updating Gillespie with controlled chaos. American Naturalist 146:479 487. Hanski, I. 1988. Four kinds of extra long diapause in insects: a review of theory and observations. Annales Zoologici Fennici 25:37 53. Hassell, M. P., J. H. Lawton, and R. M. May. 1976. Patterns of dynamic behaviour in single-species populations. Journal of Animal Ecology 45:471 486. Holt, R. D., and M. A. McPeek. 1996. Chaotic population dynamics favors the evolution of dispersal. American Naturalist 148:709 718. Hopper, K. R. 1999. Risk-spreading and bet-hedging in insect population biology. Annual Review of Entomology 44:535 560. Karban, R. 1997. Evolution of prolonged development: a life table analysis for periodical cicadas. American Naturalist 150:446 461. May, R. M. 1976. Simple mathematical models with very complicated dynamics. Nature 261:459 467. Menu, F., J. P. Roebuck, and M. Viala. 2000. Bet-hedging diapause strategies in stochastic environments. American Naturalist 155: 724 734. Newman, T. J., J. Antonovics, and H. M. Wilbur. 2002. Population dynamics with a refuge: fractal basins and the suppression of chaos. Theoretical Population Biology 62:121 128. Ricker, W. E. 1954. Effects of compensatory mortality upon population abundance. Journal of Wildlife Management 18:45 51. Ringel, M. S., M. Rees, and H. C. J. Godfray. 1998. The evolution of diapause in a coupled host-parasitoid system. Journal of Theoretical Biology 194:195 204. Sasaki, A., and S. P. Ellner. 1995. The evolutionarily stable phenotype distribution in a random environment. Evolution 49:337 350. Turchin, P., and S. P. Ellner. 2000. Living on the edge of chaos: population dynamics of Fennoscandian voles. Ecology 81:3099 3116. Van Dooren, T. J. M., and J. A. J. Metz. 1998. Delayed maturation in temporally structured populations with non-linear dynamics. Journal of Evolutionary Biology 11:41 62. Yoshida, T., L. E. Jones, S. P. Ellner, G. F. Fussmann, and N. G. Hairston. 2003. Rapid evolution drives ecological dynamics in a predator-prey system. Nature 424:303 306. Associate Editor: William F. Morris Editor: Donald L. DeAngelis