Alternative stable states in communities with intraguild predation
Introduction
Trophic levels in nature are not always clearly defined: two consumers can be competitors for a common resource and, at the same time, interact as predator and prey. This phenomenon is referred to as intraguild predation (IGP) because consumer species prey on their own “ecological guild”. Intraguild predation is a common occurrence in natural communities (Polis et al., 1989, Rosenheim et al., 1995, Arim and Marquet, 2004). In communities where two consumers compete for a shared resource, consumer coexistence is possible only if the IG prey is a superior resource competitor compared to the IG predator, because the IG predator has the advantage of being able to prey on its competitor (Polis et al., 1989, Holt and Polis, 1997). The competition—IGP trade-off is expressed at intermediate levels of resource productivity, when resource limitation favors the superior competitor but is not so strong as to exclude the IG predator. In highly productive environments, theory predicts that the IG predator excludes the prey (Holt and Polis, 1997, Diehl and Feissel, 2000, Mylius et al., 2001), though this is not always observed in nature (Mylius et al., 2001, Borer et al., 2003, Amarasekare, 2003, Amarasekare, 2007).
Alternative stable states arise when, for a given set of parameters, the community can exhibit multiple attractors. Analyses of the three-species IGP food web module have revealed that alternative states are possible, at least in theory (Holt and Polis, 1997, McCann and Hastings, 1997, Diehl and Feissel, 2000, Mylius et al., 2001, Revilla, 2002, Ruggieri and Schreiber, 2005, Takimoto et al., 2007). If alternative states exist, the long-term community composition is determined by the initial conditions; additionally, communities can jump between alternative states in response to perturbations (either rapid transient fluctuations in population size or gradual sustained changes in environmental conditions). Such abrupt transitions could affect the entire food web and have consequences for both community diversity and ecosystem stability.
Empirical evidence of alternative states in communities with IGP is scarce, largely because of the difficulty to detect them in nature. Laboratory experiments provide the best setting for testing theoretical predictions (Morin, 1999, Diehl and Feissel, 2001), although factors such as demographic stochasticity can cause discrepancies between theory and data even under controlled conditions (Montserrat et al., 2008). In a microcosm experiment of an IGP community, Morin (1999) verified that coexistence between IG predator and IG prey occurs, as predicted by theory, at intermediate levels of resource productivity; however a previous study with the same system (Lawler and Morin, 1993) found that the IG prey was excluded at lower levels of productivity. Montserrat et al. (2008) observed two different outcomes in four replicates of the same laboratory experiment on mites competing for pollen: when resources were abundant, the IG predator could exclude the IG prey (three replicates) or the IG prey excluded the IG predator (one replicate). Although many factors could explain these unexpected results, the possibility of alternative states cannot be ruled out. These two empirical examples underscore the importance of theoretical investigations that improve our ability to predict and diagnose alternative states (or, at the least, to be able to dismiss their possibility) in natural communities.
Most theory on IGP is based on population models that consider logistic or chemostat dynamics for the resource, and linear (Type I) or saturating (Type II) functional responses for the predation terms. These models exhibit three basic types of alternative states. First, IGP models with logistic resource dynamics and linear functional responses exhibit alternative states where either the IG prey or IG predator populations are stable but coexistence is not (Holt and Polis, 1997, Diehl and Feissel, 2000, Revilla, 2002). Second, IGP models with implicit resource dynamics (e.g., the Schoener model with IGP) exhibit alternative states with coexistence of IG prey and IG predator or IG predator only (Holt and Polis, 1997, Ruggieri and Schreiber, 2005). (Note that the resource function used in Ruggieri and Schreiber, 2005 corresponds to a quasi steady-state approximation to chemostat dynamics and linear functional responses.) These two types of alternative states also occur in models with chemostat resource dynamics, whether functional responses are linear (Takimoto et al., 2007) or saturating (Mylius et al., 2001). Third, IGP models with logistic resource dynamics and Type II functional responses in the consumers exhibit alternative states with IG prey only or coexistence of IG prey and IG predator. This has been previously reported by McCann and Hastings (1997) in the form of the stable resource—prey limit cycle occurring at the same time as a coexistence (chaotic) attractor. This combination also occurs in a 4-species version of the chemostat model with nonlinear functional responses (Kuijper et al., 2003) in the form of two stable equilibria. With the exception of the study by Kuijper et al. (2003), the alternative states scenario with IG prey only or coexistence has been largely overlooked in the analysis of alternative states.
While previous studies on alternative states have greatly enhanced our understanding of the dynamics of communities with IGP, the fact that different models incorporate different biological scenarios has made it difficult to derive predictions that can be empirically verified. This paper aims at developing a general conceptual framework for conducting a comparative analysis of alternative states in IGP models. We compare models with different types of resource dynamics (chemostat vs. logistic) and consumer functional responses (linear vs. saturating). Following Takimoto et al. (2007), we analyze the sequence of bifurcations along a resource productivity gradient that lead to the different combinations of alternative states. We derive analytical conditions for the existence of alternative states under different types of resource dynamics and consumer functional responses. We thus extend the work of Takimoto et al. (2007), which was limited to chemostat resource dynamics and linear functional responses. A novel feature of our work is the comparative framework, which allows us to identify the types of communities in which alternative states are most likely to be observed. Our results apply to a wide variety of communities, including insects host–parasitoid interactions, omnivorous bacteria, and fish and mammalian communities with IGP.
Section snippets
Model
A mathematical model describes interactions between three populations: the resource (R), IG prey (N), and IG predator (P). Resources are supplied logistically (S) and via immigration (I), while they are depleted by predation (or equivalently, parasitism) and emigration (E). The IG prey and IG predator engage in competition for the resource and in predator–prey interactions. In its most general form, the model is written
Asymptotic solutions
Depending on parameter values, the model can have different attractors, including stable equilibria, limit cycles, and chaotic attractors (McCann and Hastings, 1997, Tanabe and Namba, 2005). In this section we limit our analysis to finding the equilibria, in the chemostat and logistic models, and the bifurcations along the productivity gradient where their stability changes.
Conditions for alternative states
The IG prey or IG predator alternative states combination (i) will occur if the productivity level at which the predator can invade the prey is greater than the productivity level at which the prey can invade the predator. In that case there is a region where neither species can invade the other, thus IG prey and IG predator communities are both stable and mutually exclusive. The criterion for this is
In the chemostat model, this condition becomeswhich if the functional
Discussion
The occurrence of alternative states in natural communities has received much attention in recent years, particularly because of the potential for anthropogenic effects to change species abundances and cause abrupt transitions between community states (Scheffer et al., 2001, Andersen et al., 2009). While we have a good understanding of the biological conditions that give rise to alternative states in simple communities with one or two trophic levels [e.g., plant communities with preemptive
Acknowledgments
We thank the editor, two reviewers, and Kenichi Okamoto for comments. This research was funded by NSF Grant #DEB-0717350 to P.A.
References (32)
- et al.
Ecological thresholds and regime shifts: approaches to identification
Trends Ecol. Evol.
(2009) - et al.
Inverse density dependence and the Allee effect
Trends Ecol. Evol.
(1999) - et al.
Adaptive omnivory and species coexistence in tri-trophic food webs
Theor. Popul. Biol.
(2005) - et al.
Omnivory and food web dynamics
Ecol. Model.
(2003) - et al.
Ontogenetic scaling of foraging rates and the dynamics of a size-structured consumer-resource model
Theor. Popul. Biol.
(1998) Effects of intraguild predation on resource competition
J. Theor. Biol.
(2002)- et al.
Intraguild predation among biological-control agents—theory and evidence
Biol. Control
(1995) - et al.
Alternative stable states and regional community structure
J. Theor. Biol.
(2004) - et al.
Consequences of the Allee effect for behaviour, ecology and conservation
Trends Ecol. Evol.
(1999) - et al.
Intraguild predation promotes complex alternative states along a productivity gradient
Theor. Popul. Biol.
(2007)
Diversity–stability relationships in multitrophic systems: an empirical exploration
J. Anim. Ecol.
Trade-offs, temporal, variation, and species coexistence in communities with intraguild predation
Ecology
Intraguild predation: a widespread interaction related to species biology
Ecol. Lett.
Testing intraguild predation theory in a field system: does numerical dominance shift along a gradient of productivity?
Ecol. Lett.
Effects of enrichment on three-level food chains with omnivory
Am. Nat.
Intraguild prey suffer from enrichment of their resources: a microcosm experiment with ciliates
Ecology
Cited by (44)
Timing matters: Sampling frequency for early-warning indicators across food web components in a virtual lake
2023, Ecological IndicatorsMeasuring the occurrence and strength of intraguild predation in modern food webs
2020, Food WebsCitation Excerpt :Scenario ii) the coexistence of IGPconsumers or dominance by the IGpredator; scenario ii required the common resource have a chemostatic growth rate and the IGPconsumers have linear or non-linear functional responses. Scenario iii) the coexistence of IGP species or competitive dominance by the IGprey; the last alternative stable state required the common resource exhibit logistic growth and the IGPconsumers have non-linear functional responses (Verdy and Amarasekare, 2010). In a system with IGP interactions producing alternative stable states, the community can shift between scenarios in response to perturbation, thus impacting community diversity and ecosystem stability that result in changes to the structure and dynamics of entire ecosystems (Verdy and Amarasekare, 2010).
A mathematical model of intraguild predation with prey switching
2019, Mathematics and Computers in SimulationCitation Excerpt :Empirical observations have shown different stable communities depending on initial conditions [13,24,25] although other factors such as stochastic dynamics, transient dynamics, or reciprocal IGP may account for these phenomena [24]. Some studies investigating the dynamics of the IGP models have reported the existence of multiple attractors with their connection to phenomena observed in nature [32,40]. Faria and Costa [14] considered an IGP model with allochthonous resources and prey switching, and studied the effect of resource enrichment on population dynamics of the model.
Dynamics of an intraguild predation model with an adaptive IGpredator
2018, Mathematical BiosciencesForced neighbours: Coexistence between jaguars and pumas in a harsh environment
2017, Journal of Arid EnvironmentsCitation Excerpt :The third case considers intermediate resource levels and the possibility of coexistence between predators; in this scenario the intraguild prey persists despite mortality induced by the intraguild predator. All those models make the assumption that the intraguild prey is a superior competitor for the resource than the intraguild predator, since it has also the disadvantage of being itself the victim of predation (Verdy and Amarasekare, 2010). In order to survive in an intraguild predation system, intraguild prey species must obtain sufficient food but also avoid to be killed by larger predators.
Spatiotemporal dynamics and spatial pattern in a diffusive intraguild predation model with delay effect
2017, Applied Mathematics and ComputationCitation Excerpt :Abrams and Fung [14] investigated prey persistence and mainly provided numerical simulation for a kind of IGP models with Holling type-II functional responses. Verdy and Amarasekare [15] and Freeze et al. [16] investigated Holling type-II and ratio-dependent functional responses, respectively. Kang and Wedekin [17] considered Holling-III functional response for predation on the IG prey by the IG predator in two kinds of models, which one is called IGP model with specialist predator and the other is called IGP model with generalist predator.