Skip to main content

Advertisement

Log in

Complex Dynamics in an Eco-epidemiological Model

  • Original Article
  • Published:
Bulletin of Mathematical Biology Aims and scope Submit manuscript

Abstract

The presence of infectious diseases can dramatically change the dynamics of ecological systems. By studying an SI-type disease in the predator population of a Rosenzweig–MacArthur model, we find a wealth of complex dynamics that do not exist in the absence of the disease. Numerical solutions indicate the existence of saddle–node and subcritical Hopf bifurcations, turning points and branching in periodic solutions, and a period-doubling cascade into chaos. This means that there are regions of bistability, in which the disease can have both a stabilising and destabilising effect. We also find tristability, which involves an endemic torus (or limit cycle), an endemic equilibrium and a disease-free limit cycle. The endemic torus seems to disappear via a homoclinic orbit. Notably, some of these dynamics occur when the basic reproduction number is less than one, and endemic situations would not be expected at all. The multistable regimes render the eco-epidemic system very sensitive to perturbations and facilitate a number of regime shifts, some of which we find to be irreversible.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Fig. 1
Fig. 2
Fig. 3
Fig. 4
Fig. 5
Fig. 6
Fig. 7
Fig. 8

Similar content being viewed by others

References

  • Bate, A. M., & Hilker, F. M. (2013). Predator–prey oscillations can shift when diseases become endemic. J. Theor. Biol., 316, 1–8.

    Article  MathSciNet  Google Scholar 

  • Beardmore, I., & White, K. A. J. (2001). Spreading disease through social groupings in competition. J. Theor. Biol., 212, 253–269.

    Article  Google Scholar 

  • Begon, M., Bennett, M., Bowers, R. G., French, S. M., Hazel, N. P., & Turner, J. (2002). A classification of transmission terns in host-microparasite models: numbers, densities and areas. Epidemiol. Infect., 129, 147–153.

    Article  Google Scholar 

  • Berezovskaya, F. S., Song, B., & Castillo-Chavez, C. (2010). Role of prey dispersal and refuges on predator–prey dynamics. SIAM J. Appl. Math., 70, 1821–1839.

    Article  MATH  MathSciNet  Google Scholar 

  • Berryman, A. A., & Millstein, J. A. (1989). Are ecological systems chaotic—and if not, why not? Trends Ecol. Evol., 4, 26–28.

    Article  Google Scholar 

  • Biggs, R., Carpenter, S. R., & Brock, W. A. (2009). Turning back from the brink: detecting an impending regime shift in time to avert it. Proc. Natl. Acad. Sci. USA, 106, 826–831.

    Article  Google Scholar 

  • Chattopadhyay, J., & Bairagi, N. (2001). Pelicans at risk in Salton Sea—an eco-epidemiological model. Ecol. Model., 136, 103–112.

    Article  Google Scholar 

  • Ferrari, M. J., Perkins, S. E., Pomeroy, L. W., & Bjørnstad, O. N. (2011). Pathogens, social networks, and the paradox of transmission scaling. Interdiscip. Perspect. Infect. Dis., 2011, 267049.

    Google Scholar 

  • Gilpin, M. E. (1979). Spiral chaos in a predator–prey model. Am. Nat., 113, 306–308.

    Article  MathSciNet  Google Scholar 

  • González-Olivares, E., & Rojas-Palma, A. (2011). Multiple limit cycles in a Gause type predator–prey model with Holling type III functional response and Allee effect on prey. Bull. Math. Biol., 73, 1378–1397.

    Article  MATH  MathSciNet  Google Scholar 

  • Hastings, A., & Powell, T. (1991). Chaos in a three-species food chain. Ecology, 72, 896–903.

    Article  Google Scholar 

  • Hilker, F. M., & Malchow, H. (2006). Strange periodic attractors in prey–predator system with infected prey. Math. Popul. Stud., 13, 119–134.

    Article  MATH  MathSciNet  Google Scholar 

  • Hilker, F. M., & Schmitz, K. (2008). Disease-induced stabilization of predator–prey oscillations. J. Theor. Biol., 225, 299–306.

    Article  Google Scholar 

  • Hilker, F. M., Langlais, M., & Malchow, H. (2009). The Allee effect and infectious diseases: extinction, multistability, and the (dis-)appearance of oscillations. Am. Nat., 173, 72–88.

    Article  Google Scholar 

  • Hurtado, P. J., Hall, S. R., & Ellner, S. P. (2013). Infectious disease in consumer populations: dynamic consequences of resource-mediated transmission and infectiousness, manuscript in review.

  • Kooi, B. W., van Voorn, G. A. K., & Das, K. p. (2011). Stabilization and complex dynamics in a predator–prey model with predator suffering from an infectious disease. Ecol. Complex., 8, 113–122.

    Article  Google Scholar 

  • Kuznetsov, Y. A. (1995). Elements of applied bifurcation theory. New York: Springer.

    Book  MATH  Google Scholar 

  • May, R. (1974). Biological populations with nonoverlapping generations: stable points, stable cycles, and chaos. Science, 186, 645–647.

    Article  Google Scholar 

  • McCallum, H., Barlow, N., & Hone, J. (2001). How should pathogen transmission be modelled? Trends Ecol. Evol., 16, 295–300.

    Article  Google Scholar 

  • Rosenzweig, M. L., & MacArthur, R. H. (1963). Graphical representation and stability conditions of predator–prey interactions. Am. Nat., 97, 209–223.

    Article  Google Scholar 

  • Scheffer, M. (2009). Critical transitions in nature and society. Princeton: Princeton University Press.

    Google Scholar 

  • Seydel, R. (1988). From equilibrium to chaos—practical bifurcation and stability analysis. New York: Elsevier.

    MATH  Google Scholar 

  • Sieber, M., & Hilker, F. M. (2011). Prey, predators, parasites: intraguild predation or simpler community modules in disguise? J. Anim. Ecol., 80, 414–421.

    Article  Google Scholar 

  • Siekmann, I., Malchow, H., & Venturino, E. (2010). On competition of predators and prey infection. Ecol. Complex., 7, 446–457.

    Article  Google Scholar 

  • Stiefs, D., Venturino, E., & Feudel, U. (2009). Evidence of chaos in eco-epidemic model. Math. Biosci. Eng., 6, 855–871.

    Article  MATH  MathSciNet  Google Scholar 

  • Thomas, W. R., Pomerantz, M. J., & Gilpin, M. E. (1980). Chaos, asymmetric growth and group selection for dynamical stability. Ecology, 61, 1312–1320.

    Article  Google Scholar 

  • Upadhyay, R. K., Bairagi, N., Kundu, K., & Chattopadhyay, J. (2008). Chaos in eco-epidemiological problem of the Salton Sea and its possible control. Appl. Math. Comput., 196, 392–401.

    Article  MATH  MathSciNet  Google Scholar 

  • van den Driessche, P., & Watmough, J. (2002). Reproductive numbers and sub-threshold endemic equilibria for compartmental models of disease transmission. Math. Biosci., 180, 29–48.

    Article  MATH  MathSciNet  Google Scholar 

Download references

Acknowledgements

The authors would like to thank Faina Berezovsky and an anonymous reviewer for their constructive comments.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Andrew M. Bate.

Appendix: Steady States of FD and DD Models

Appendix: Steady States of FD and DD Models

There are two key differences between the DD and FD model. One is the existence of a disease-induced extinction of the predator in the FD model. The other is that there can be only one coexistent steady state in the FD model as the corresponding value of i is known; whereas in the DD model, there can be one or two coexistent steady states.

1.1 A.1 Trivial/Semi-trivial Steady States

  • Both models: (0,0,0) which always exists and is always unstable.

  • Both models: (1,0,0) which always exists and is stable if \(m>\frac{1}{1+h}\), unstable otherwise.

  • Both models: (N ,P ,0), where \(N^{*}=\frac{hm}{1-m}\) and P =r(h+N )(1−N ). This exists when \(m<\frac{1}{1+h}\) (<1). It is stable if \(N^{*}>\frac{1-h}{2}\) (equivalently \(m>\frac{1-h}{1+h}\) (Hopf bifurcation)) and \(R_{0}^{*}<1\), where \(R_{0}^{*}\) equals \(\frac{\beta P^{*}}{m+\mu}\) (DD model) and \(\frac{\beta}{m+\mu}\) (FD model).

  • FD model only: (1,0,i ) where \(i^{*}=1-\frac{1}{(\beta-\mu )(1+h)}\). This exists when \(\beta-\mu>\frac{1}{1+h}\) and is stable if \(m+\mu i^{*}>\frac{1}{1+h}\), unstable otherwise.

  • (FD model only: (0,0,1). This is always unstable.)

  • (FD model only: (0,0,i ). i is unspecified. This only exists when β=μ, which is not generally true. This is always unstable.)

1.2 A.2 Coexistent Steady State(s)

1.2.1 A.2.1 DD Model

The coexistent equilibria for the DD model are of the form (N ,P ,i ), where \(N^{*}=\frac{h(m+\mu i^{*})}{1-(m+\mu i^{*})}\), P =r(h+N )(1−N ) and \(i^{*}=1-\frac{N^{*}}{h+N^{*}}\frac{1}{\beta P^{*}-\mu }=1-\frac{m+\mu i^{*}}{\beta P^{*}-\mu}=\frac{\mu(1-i^{*})-m+\beta P^{*}}{\beta P^{*}-\mu}\). This exists when \(i^{*}<\frac{1-m}{\mu}\) (N >0), \(i^{*}<\frac{1}{\mu(h+1)}-\frac{m}{\mu}\) (N <1, i.e. P >0), \(P^{*}>\frac{\mu}{\beta}\) (for i <1) and \(P^{*}>\frac{\mu+m}{\beta}\) (for i >0).

The strongest of these conditions are \(i^{*}<\frac{1}{\mu(h+1)}-\frac {m}{\mu}\) and \(P^{*}>\frac{\mu+m}{\beta}\), which are the conditions that \(R^{p}_{i}>1\) (the predators’ reproductive number given an infection is present) and \(R_{0}^{*}>1\), (the diseases’ reproductive number).

It is not clear whether (N ,P ,i ) has only one solution. Consequently, this must be solved. For tidiness, let D=m+μi . Starting with \(\frac{D-m}{\mu}\) (=i ), we get:

$$\begin{aligned} \frac{D-m}{\mu}&=1-\frac{D}{\beta P-\mu} \end{aligned}$$
(16)
$$\begin{aligned} &=1-\frac{D}{\beta r (h+N)(1-N)-\mu} \end{aligned}$$
(17)
$$\begin{aligned} &=1-\frac{D}{\beta r (h+\frac{hD}{1-D})(1-\frac{hD}{1-D})-\mu} \end{aligned}$$
(18)
$$\begin{aligned} &=1-\frac{D(1-D)^2}{\beta r h(1-D-hD) -\mu(1-D)^2}. \end{aligned}$$
(19)

After some further rearrangement, we get:

$$ 0= \biggl(\frac{D-m}{\mu}-1 \biggr)\beta r h(1-D-hD)+(m+\mu) (1-D)^2. $$
(20)

This is clearly quadratic with respect to D, and thus i . D can only be biologically realistic if D∈(m,m+μ) (i.e. i ∈(0,1)). This means there are at most two feasible coexistent solutions.

The stability is not fully investigated. However, when these steady states exist, no other steady state is stable. Also, when there are two viable coexistent steady states, they will be connected to a nearby saddle–node bifurcation, so only one steady state should be stable. Given this, we expect would that either one of the coexistent equilibria is stable or there is some stable periodic solution.

1.2.2 A.2.2 FD Model

The coexistent steady state for the FD model is (N ,P ,i ) where \(N^{*}=\frac{h(m+\mu i^{*})}{1-(m+\mu i^{*})}\), P =r(h+N )(1−N ) and \(i^{*}=1-\frac{\mu+m}{\beta}\). This exists when β>μ+m (i >0), \(i^{*}<\frac{1-m}{\mu}\) (N >0), \(i^{*}<\frac {1}{\mu(h+1)}-\frac{m}{\mu}\) (N <1, i.e. P >0). Like the DD model, the two strongest conditions are \(i^{*}<\frac{1}{\mu(h+1)}-\frac {m}{\mu}\) and β>μ+m. In this case, there is only one coexistent steady state if it exists.

The stability is not fully investigated. However, when this steady state exists, no other steady state is stable. Given this, we would expect that either one of the coexistent equilibria is stable or there is some stable periodic solution.

Rights and permissions

Reprints and permissions

About this article

Cite this article

Bate, A.M., Hilker, F.M. Complex Dynamics in an Eco-epidemiological Model. Bull Math Biol 75, 2059–2078 (2013). https://doi.org/10.1007/s11538-013-9880-z

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s11538-013-9880-z

Keywords

Navigation