Topological structure and interaction strengths in model food webs
Introduction
Food webs, which represent the links between predators and prey in an ecological community, are complex networks which present several problems to the modeller. Firstly, can the range and nature of webs be specified a priori, perhaps using some generic biological principles? Secondly, can a dynamics describing the change in population sizes of species in the web be defined on the network? Thirdly, given that the number of links in a food web of a reasonable size will be of the order of several hundred, is it possible in practice, or even desirable, to give values to all of these link strengths?
The formidable difficulties associated with answering these questions led most early researchers to adopt approaches to the modelling of food webs which either bypassed some of these questions entirely, or implemented them in a very simple way. For example, May (1973) assumed the network to be a random graph, the interactions to be of randomly chosen strength and linearised the dynamics near a fixed point. Other food web modellers ignored the dynamics completely and simply gave rules to construct static graphs Cohen et al., 1990, Williams and Martinez, 2000. Even in the recent flurry of interest concerning network structure and topology (Albert and Barabási, 2002), most modellers have concentrated on specifying the nature of the network, rather than defining the dynamics on the network. The problem with this approach is that there is no reason why network structures which are appealing or which are found in social or other networks (small world, scale invariance) should apply to food webs. A recent study indeed shows that this is the case (Dunne et al., 2002a).
This suggests a more sophisticated approach to the modelling of food webs should be adopted. A clue as to how we might move forward is that it is clear that the structure of the network depends on the dynamics of the network, and cannot be divorced from it. It is therefore not appropriate to specify the web and then define dynamics—the two are interdependent. For example, a predator–prey link between any two species will disappear if either of the species becomes extinct and this will depend on the nature of the population dynamics that is chosen to govern their interaction. It is also clear that the dynamics on the network will be strongly influenced by the nature of the network itself. This strongly suggests that we cannot separate the population dynamics on the network from the dynamics which changes the network structure, which will occur on much longer time scales.
These comments address the first two of the questions posed at the beginning of this section, but there still remains the difficulty of knowing how to generate the several hundred quantities which specify the parameters in the model dynamics at any given time. The solution to this problem which we favour is to assemble the food web from one (or very few) species, so that the parameters are determined by the dynamics of web assembly. We have already explained that this dynamics is inextricably linked to the population dynamics. Starting with only one species simply amounts to giving an initial condition to the dynamics. In this way we determine those food web structures that can actually be reached rather than simply those that are possible.
This approach combines the reductionist and holistic treatments of ecosystems. We specify the rules that govern the dynamics of the interacting species in our communities but we then let the system itself parameterise those rules, and thus the ecosystem structure is an emergent property of the system. In this way we avoid having to deal with the intractable complexity of real ecosystems whilst still simulating the complexity of behaviour they exhibit (Jørgensen et al., 1992).
A model based on this philosophy was developed by some of us a few years ago and has been under study since then. An original version of the model (Caldarelli et al., 1998) was superseded by a later version with more realistic population dynamics (Drossel et al., 2001), and reviews which discuss the model specifically (Quince et al., 2002) and in a more general context (Drossel and McKane, 2003) are available. Our aim in this paper is to present a more extensive set of results from the model, emphasising aspects that were not stressed in previous investigations. A prime example is the distribution of link strengths, which is a topic which has been discussed extensively in the last year or so (Berlow et al., 2004) and which is an emergent attribute in our model, and consequently a fundamental test of the whole approach.
We begin by outlining the model in Section 2 and then, in order to provide some intuition on how a particular web is built up, we describe the time evolution of a single web in Section 3. The structure of the model food webs which are dynamically constructed through simulation of the model are explored in Section 4 and compared with data in Section 5. The distribution of link strengths in the model is explored in Section 6 and a discussion of our broad conclusions, as well as possible future avenues of investigation, is given in Section 7.
Section snippets
The model
In this section we will give an overview of the model, presenting enough detail that subsequent sections of the paper may be understood. Readers should consult Drossel et al. (2001) for further details, especially regarding motivation for various model choices and the specifics of the computer simulation.
The model is unusual in spanning a very large range of time scales, from changes in foraging strategies—which might occur on a time scale of the order of days—to evolutionary time scales. As we
Time evolution of an individual simulation
The mechanism summarised in Fig. 1 is capable of generating large complex food webs. This is true for a wide range of parameter space—the boundaries of which we explore in the next section. In Fig. 2 the time evolution, measured in number of attempted speciation events, of the species number is shown for one of these sets of parameter values. For these values of the parameters, the number of species initially increases quite rapidly but with sizable fluctuations. Then after about 10,000
The structure of the model food webs
In the previous section it was argued that after a large enough number of speciation events the model generated food web structures from an individual simulation will be drawn from an approximately stationary distribution. It is this stationary distribution of structures that we are interested in here. Our aim is to provide a qualitative understanding of the structures and the processes that generate them. This will be done by presenting, for a range of parameter values, both individual
Comparison to empirical food webs
The food webs constructed from simulations of the model have been compared to empirical food webs in earlier publications Caldarelli et al., 1998, Drossel et al., 2001. The emphasis in these earlier papers was on comparing the percentage of species which were basal (having no prey), intermediate (having both prey and predators) and top (having no predators) and the percentage of predator–prey links which connected species of this type. Agreement was generally good, with the exception of the
Interaction strengths in model food webs
The majority of the food web statistics examined in the previous sections take no account of the strength of the predator–prey interactions in the model generated communities. They describe properties of binary food webs for which a link is either present or absent. This approach was adopted for reasons of simplicity and to facilitate comparison with the empirical data, where for most well resolved food webs the strengths of the interactions are not known. For those natural communities for
Discussion
In this paper we have reported the results of performing a very large number of simulations on a model of a coevolving multispecies community in order to generate food webs. The results obtained were considerably more extensive than those reported in earlier publications. They were also complementary: in Drossel et al. (2001) the emphasis was on comparing model webs with empirical webs by looking at the number of top, intermediate and basal species and the links between them. The aim was to
Acknowledgements
We wish to thank Jennifer Dunne, Mark Huxham and Phillip Warren for supplying food web data. CQ wishes to thank the EPSRC (UK) for financial support during the early part of this work.
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