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Individual behavioral variation in predator–prey models

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Ecological Research

Abstract

The role of individual behavioral variation in community dynamics was studied. Behavioral variation in this study does not refer to differences in average responses (e.g., average response between presence and absence of antipredator behavior). Rather it refers to the variation around the average response that is not explained by trivial experimental treatments. First, the effect of behavioral variation was examined based on Jensen’s inequality. In cases of commonly used modeling framework with type II functional response, neglecting behavioral variation (a component of encounter rate) causes overestimation of predation effects. The effect of this bias on community processes was examined by incorporating the behavioral variation in a commonly used consumer-resource model (Rosenzweig–MacArthur model). How such a consideration affects a model prediction (paradox of enrichment) was examined. The inclusion of behavioral variation can both quantitatively and qualitatively alter the model characteristics. Behavioral variation can substantially increase the stability of the community with respect to enrichment.

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Fig. 1
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Fig. 3a–d
Fig. 4a,b

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References

  • Abrams PA (1992) Predators that benefit prey and prey that harm predators: unusual effects of interacting foraging adaptations. Am Nat 140:573–600

    Article  Google Scholar 

  • Abrams PA, Ginzburg LR (2000) The nature of predation: prey dependent, or ratio dependent or neither? Trends Ecol Evol 15:337–341

    Article  PubMed  Google Scholar 

  • Abrams PA, Vos M (2003) Adaptation, density dependence, and the abundances of trophic levels. Evol Ecol Res 5:1113–1132

    Google Scholar 

  • Abrams PA, Walters CJ (1996) Invulnerable prey and the paradox of enrichment. Ecology 77:1125–1133

    Article  Google Scholar 

  • Andersen T, Elser JJ, Hessen DO (2004) Stoichiometry and population dynamics. Ecol Lett 7:884–900

    Article  Google Scholar 

  • Anholt BR, Werner E, Skelly DK (2000) Effect of food and predators on the activity of four larval ranid frogs. Ecology 81:3509–3521

    Google Scholar 

  • Barnes MC, Persons MH, Rypstra AL (2002) The effect of predator chemical cue age on antipredator behavior in the wolf spider Pardosa milvina (Aranae: Lycosidae). J Insect Behav 15:269–280

    Article  Google Scholar 

  • Beddington JR (1975) Mutual interference between parasites and predators and its effect on searching efficiency. J Anim Ecol 44:331–340

    Article  Google Scholar 

  • Bohannan BJM, Lenski RE (1997) Effect of resource enrichment on a chemostat community of bacteria and bacteriophage. Ecology 78:2303–2315

    Article  Google Scholar 

  • Bolker BM, Pacala SW, Levin SA (2000) Moment methods for stochastic processes in continuous space and time. In: Dieckmann U, Law R, Metz JAJ (eds) The geometry of ecological interactions. Cambridge University Press, Cambridge, pp 388–411

    Google Scholar 

  • Bolker B, Holyoak M, Krivan V, Rowe L, Schmitz O (2003) Connecting theoretical and empirical studies of trait-mediated interactions. Ecology 84:1101–1114

    Article  Google Scholar 

  • Caro T (2005) Antipredator defenses in birds and mammals. University of Chicago Press, Chicago

    Google Scholar 

  • Dall SRX, Giraldeau LA, Olsson O, McNamara JM, Stephens DW (2005) Information and its use by animals in evolutionary ecology. Trends Ecol Evol 20:187–193

    Article  PubMed  Google Scholar 

  • DeAngelis DL, Goldstein RA, O’Neil RV (1975) A model for trophic interaction. Ecology 56:881–892

    Article  Google Scholar 

  • de Roos AM, Persson L, McCauley E (2003) The influence of size-dependent life history traits on the structure and dynamics of populations and communities. Ecol Lett 6:473–387

    Article  Google Scholar 

  • Fussmann GF, Ellner SP, Shertzner KW, Hairston NG Jr (2000) Crossing the Hopf bifurcation in a live predator-prey system. Science 290:1358–1360

    Article  PubMed  CAS  Google Scholar 

  • Genkai-Kato M, Yamamura N (1999) Unpalatable prey resolves the paradox of enrichment. Proc R Soc London B 266:1215–1219

    Article  Google Scholar 

  • Hastings A (1997) Population biology. Springer, New York

    Google Scholar 

  • Holling CS (1959) Some characteristics of simple types of predation and parasitism. Can Entomol 91:385–398

    Google Scholar 

  • Inouye BD (2005) The importance of the variance around the mean effect size of ecological processes: comment. Ecology 86:262–265

    Article  Google Scholar 

  • Jensen CXJ, Ginzburg LR (2005) Paradoxes or theoretical failures? The jury is still out. Ecol Model 188:3–14

    Article  Google Scholar 

  • Kagawa Y, Maeto K (2007) Laboratory-based study on the predatory ability of Carabus yaconinus (Coleoptera: Carabidae) on larvae of Spodoptera litura (Lepidoptera: Noctuidae). Appl Entomol Zool 42:49–53

    Article  Google Scholar 

  • Krebs JR, Erichsen JT, Webber MI, Charnov EL (1977) Optimal prey-selection by the great tit (Parus major). Anim Behav 25:30–38

    Article  Google Scholar 

  • Lima SL, Dill LM (1990) Behavioral decisions made under the risk of predation: a review and prospects. Can J Zool 68:619–640

    Article  Google Scholar 

  • Murdoch WW, Nisbet RM, McCauley E, deRoos AM, Gurney WSC (1998) Plankton abundance and dynamics across nutrient levels: tests of hypotheses. Ecology 79:1339–1356

    Google Scholar 

  • Murdoch WW, Briggs CJ, Nisbet RM (2003) Consumer-resource dynamics. Monographs in population biology. Princeton University Press, Princeton

    Google Scholar 

  • Putra NS, Yasuda H (2006) Effects of prey species and its density on larval performance of two species of hoverfly larvae, Episyrphus balteatus de Geer and Eupeodes corollae Fabricus (Diptera: Syrphidae). Appl Entomol Zool 41:389–397

    Article  Google Scholar 

  • Rosenzweig ML (1971) Paradox of enrichment: destabilization of exploitation ecosystems in ecological time. Science 171:385–387

    Article  PubMed  CAS  Google Scholar 

  • Rosenzweig ML, MacArthur RH (1963) Graphical representation and stability condition for predator-prey interactions. Am Nat 97:209–223

    Article  Google Scholar 

  • Rossi MN, Reigada C, Godoy WAC (2006) The effect of hunger level on predation dynamics in the spider Nesticodes rufipes: a functional response study. Ecol Res 21:617–623

    Article  Google Scholar 

  • Ruel JJ, Ayres MP (1999) Jensen’s inequality predicts effects of environmental variation. Trends Ecol Evol 14:361–366

    Article  PubMed  Google Scholar 

  • Ruxton GD (2005) Increasing search rate over time may cause a slower than expected increase in prey encounter rate with increasing prey density. Biol Lett 1:133–135

    Article  PubMed  Google Scholar 

  • Stephens DW (1985) How important are partial preferences? Anim Behav 33:667–669

    Article  Google Scholar 

  • Stephens DW, Krebs JR (1986) Foraging theory. Princeton University Press, Princeton

    Google Scholar 

  • Travis JMJ, Palmer SCF (2005) Spatial processes can determine the relationship between prey encounter rate and prey density. Biol Lett 1:136–138

    Article  PubMed  CAS  Google Scholar 

  • Tuljapurkar S, Caswell H (1997) Structured-population models in marine, terrestrial, and freshwater systems. Thomson, New York

    Google Scholar 

  • Turchin P (2003) Complex population dynamics: a theoretical/empirical synthesis. Monographs in population biology. Princeton University Press, Princeton

    Google Scholar 

  • Vos M, Flik BJG, Vijverberg J, Ringelberg J, Mooij WM (2002) From inducible defences to population dynamics: modelling refuge use and life history changes in Daphnia. Oikos 99:386–396

    Article  Google Scholar 

  • Vos M, Kooi W, DeAngelis DL, Mooji WM (2004a) Inducible defenses and the paradox of enrichment. Oikos 105:471–480

    Article  Google Scholar 

  • Vos M, Verschoor AM, Wäckers FL, DeAngelis DL, Mooji WM (2004b) Inducible defenses and trophic structure. Ecology 85:2783–2794

    Article  Google Scholar 

  • Werner EE, Peacor SD (2003) A review of trait-mediated indirect interactions in ecological communities. Ecology 84:1083–1100

    Article  Google Scholar 

Download references

Acknowledgments

I thank Ben Bolker, Chris Jensen, and an anonymous reviewer for their insightful comments.

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Correspondence to Toshinori Okuyama.

Appendix: Model from Genkai-Kato and Yamamura (1999)

Appendix: Model from Genkai-Kato and Yamamura (1999)

There are two prey species R 1 and R 2 and predators N that consume them.

$$ \frac{{\text{d}R_{1} }} {{\text{d}t}} = r_{1} R_{1} {\left( {\frac{{K_{1} - R_{1} - \alpha _{{12}} R_{2} }} {{K_{1} }}} \right)} - \frac{{p_{1} C_{1} R_{1} N}} {{1 + p_{1} C_{1} h_{1} R_{1} + p_{2} C_{2} h_{2} R_{2} }} $$
(8)
$$ \frac{{\text{d}R_{2} }} {{\text{d}t}} = r_{2} R_{2} {\left( {\frac{{K_{2} - \alpha _{{21}} R_{1} - R_{2} }} {{K_{2} }}} \right)} - \frac{{p_{2} C_{2} R_{2} N}} {{1 + p_{1} C_{1} h_{1} R_{1} + p_{2} C_{2} h_{2} R_{2} }} $$
(9)
$$ \frac{{\text{d}N}} {{\text{d}t}} = \frac{{b_{1} p_{1} C_{1} R_{1} N}} {{1 + p_{1} C_{1} h_{1} R_{1} + p_{2} C_{2} h_{2} R_{2} }} + \frac{{b_{2} p_{2} C_{2} R_{2} N}} {{1 + p_{1} C_{1} h_{1} R_{1} + p_{2} C_{2} h_{2} R_{2} }} - dN $$
(10)

Parameter description follows the basic model described in the main text. New parameters are competition coefficients, α12 and α21 that describe the competitive effect of prey species 2 on species 1 and vice versa, respectively. p 1 and p 2 are the probability that predators will attack prey species 1 and species 2, respectively. For this behavioral strategy of predators, optimal foraging behavior was assumed. Assuming that species 1 is more profitable (i.e., b 1/h 1 > b 2/h 2), predators should always attack species 1 (i.e., p 1 = 1). The theory suggests that p 2 is either 0 or 1 and does not hold an intermediate value (Stephens and Krebs 1986) and can be determined by the following rule,

$$ p_{2} = \left\{ {\begin{array}{*{20}c} {0} \\ {1} \\ \end{array} } \right.\begin{array}{*{20}c} {{}} \\ {{}} \\ \end{array} \begin{array}{*{20}l} {{{\text{if}}}} \\ {{{\text{otherwise}}}} \\ \end{array} \begin{array}{*{20}c} {{\frac{{b_{1} C_{1} R_{1} }} {{1 + C_{1} h_{1} R_{1} }} > \frac{{b_{2} }} {{R_{2} }}}} \\ {{}} \\ \end{array} $$
(11)

Parameter values used in this study were r 1 = 0.5, r 2 = 0.25, d = 0.25, α12 = 0.1, α21 =  0.4, C 1 = C 2 = 1, b 1 = b 2 = 0.5, h 1 = 1, h 2 = 2.083. In Fig. 3b, dynamics for R 1 and N is plotted. For the model with behavioral variance, the same parameter values for the prey species 1 were used.

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Okuyama, T. Individual behavioral variation in predator–prey models. Ecol Res 23, 665–671 (2008). https://doi.org/10.1007/s11284-007-0425-5

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