The role of parasitoids in a nursery-pollinator system: A population dynamics model
Graphical abstract
Introduction
Probably the most paradigmatic mutualistic system is pollination (Toby Kiers et al., 2010, Holland et al., 2002), in which the flower visitors obtain trophic resources (nectar, pollen, oils, etc.) and the plant obtains reproductive benefits through pollen dispersal and seed production. A special case of pollination, called nursery pollination, is reported when one pollinator species uses the fertilized flowers as hatching nests for its eggs, and the developing seeds serve as a food resource for its larvae. Therefore, the pollinating-seed predator obtains plant food resources for both its adult and larval stages, depriving the plant of part of the reproductive benefits obtained in a legitimate pollination interaction (Bronstein, 2001). Although this kind of interaction sounds eccentric, nursery pollination had been described in several families of angiosperms, with classic examples like fig trees-fig wasps and yuccas-yucca moths (Dufaÿ and Anstett, 2003). In these systems, there must exist a subtle balance between the benefits (pollination) and costs (seed predation) to achieve a positive net outcome to the plant. Indeed, the balance may shift from positive to negative, and therefore from mutualism to antagonism, depending on the mechanisms evolved by the hosts to avoid over-exploitation and on the ecological context where the interaction takes place (Leung and Poulin, 2008).
One mechanism controlling over-exploitation by the plant consists of random abortion of fruits, or selective abortion of fruits containing eggs or larvae of the pollinating-seed predator. This feature has been argued, by mathematical modeling approaches, as an evolutionary strategy of interspecific population regulation (Holland and DeAngelis, 2001, Holland and DeAngelis, 2006, Westerbergh and Westerbergh, 2001). With respect to the ecological context, apart from regulation of population densities due to environmental fluctuations, a central topic is related to the presence of third partners. One central consideration is whether the seed predator is also the unique pollinator or not (hereafter, obligate and facultative nursery pollination systems, respectively). In facultative systems, the occurrence of co-pollinators can shift the sign of this interaction, because they contribute to seed production without the cost of seed predation (Thompson and Pellmyr, 1992). The nursery pollination system may be also affected by the existence of predators, pathogens and parasitoids that may regulate the population size of the pollinating-seed predator, avoiding excess seed loss and system instability. Several field studies suggest this kind of regulatory process in nursery pollination systems (Force and Thompson, 1984, Elzinga et al., 2003, Crabb and Pellmyr, 2006, Nunes et al., 2018), but it has not been tested by population dynamic models.
Complex biological systems such as the nursery pollination are paradigmatic frameworks because different actors can play a vital role in the equilibrium of the ecological system, and the importance of an apparently secondary species can be addressed using population dynamic modeling (Neuhauser and Fargione, 2004, Holland et al., 2002). In this study, we use a generalized version of the model of García-Algarra et al. (2014), which can describe multiple ecological interactions within the same equations. This approach has the advantage of treating species interactions based on fundamental ecological laws (Turchin, 2003) and independently of the model, i.e. without having to consider them as different phenomena, which is a conceptual burden. Such a generalization may allow researchers a better representation of ecological systems by including most observed interactions, weighting their importance where necessary and avoiding frameworks of specific systems and ad hoc modeling.
We hypothesize that, when the population density of two species can alternate the net effect of their interaction between mutualism and parasitism, the presence of a third species can regulate their population dynamics and stabilize the interaction towards mutualism. To test this prediction, we applied a generalized model of ecological relations to the system made up of Caryophyllaceous plants, the nursery pollinator Hadena moths and their parasitoid wasps. We expect that a subtle regulation of the moths population by its parasitoids may stabilize the dynamics of the system, allowing the high metabolic costs of other regulatory processes, like fruit abortion, to control over-exploitation.
Section snippets
Materials and methods
We first describe the ecological system studied to build a conceptual diagram that we used to model the system with a set of differential equations.
The three populations system (no parasitoids)
By setting b34 = 0 and b43 = 0, we evaluated how the system behaves in the absence of parasitoids. In this case, the plant-nursery pollinator system had only two stable solutions, which might oscillate at first but stabilized later. One stable solution was obvious -extinction of all the populations-, and the other was a stable coexistence of plants, male moths and female moths (Fig. 3), in which the plant population declined to almost the extinction, before arose again. Even though there were
Discussion
We used a system of differential equations based on a generalization of the model of García-Algarra et al. (2014) to simulate a complex biological system with facultative mutualism, obligate mutualism, and predation. These ecological interactions can be introduced in the model simply by modifying the sign of the parameters. Since biological parameters are easily identifiable in this model, we have effectively simulated an ecological system of two species that shift along a mutualism-antagonism
Conflict of interest
The authors declare that there are no conflicts of interest regarding the publication of this paper.
Acknowledgements
This work was supported by Ministry of Economy and Competitiveness of Spain (research projects CGL2009-08755 and MTM2015-63914-P).
References (37)
- et al.
Modeling bumble bee population dynamics with delay differential equations
Ecol. Model.
(2017) - et al.
Rethinking the logistic approach for population dynamics of mutualistic interactions
J. Theor. Biol.
(2014) - et al.
The population dynamics of potato cyst nematodes
Ecol. Model.
(2007) - et al.
A mutualism-parasitism continuum model and its application to plant-mycorrhizae interactions
Ecol. Model.
(2004) - et al.
Ten years of progress in the study of Hadena-Caryophyllaceae nursery pollination, A review in light of new Mediterranean data
Flora
(2017) Making best use of model evaluations to compute sensitivity indices
Comput. Phys. Commun.
(2002)- et al.
Variance based sensitivity analysis of model output. design and estimator for the total sensitivity index
Comput. Phys. Commun.
(2010) Global sensitivity indices for nonlinear mathematical models and their Monte Carlo estimates
Math. Comput. Simul.
(2001)- et al.
The Ecology and Genetics of a Host Shift: Microbotryum as a Model System
Am. Nat.
(2002) - et al.
Impact of Flowering Phenology of Silene alba and S. dioica on Susceptibility to Fungal Infection and Seed Predation
Oikos
(1996)
The Evolution of an Invasive Plant: An Experimental Study with Silene latifolia
Ecology
The costs of mutualism
Am. Zool.
Benefits and costs to pollinating, seed-eating insects: the effect of flower size and fruit abortion on larval performance
Oecologia
Conflicts between Plants and Pollinators That Reproduce within Inflorescences: Evolutionary Variations on a Theme
Oikos
Enhanced frugivory on invasive Silene latifolia in its native range due to increased oviposition
J. Ecol.
The rearing of the gregarious koinobiont endoparasitoid Microplitis tristis (Hymenoptera: Braconidae) on its natural host Hadena bicruris (Lepidoptera: Noctuidae)
Proceedings of the Section Experimental and Applied Entomology of the Netherlands Entomological Society
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