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Determination of Keystone Species in CSM Food Web: a Topological Analysis of Network Structure

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Determination of Keystone Species in CSM Food Web: a Topological Analysis of Network Structure Network Biology, 2015, 5(1): 13-33 Article Determination of keystone species in CSM food web: A topological analysis of network structure LiQin Jiang1, WenJun Zhang1,2 1School of Life Sciences, Sun Yat-sen University, Guangzhou 510275, China 2International Academy of Ecology and Environmental Sciences, Hong Kong E-mail: [email protected], [email protected] Received 20 August 2014; Accepted 28 September 2014; Published online 1 March 2015 Abstract The importance of a species is correlated with its topological properties in a food web. Studies of keystone species provide the valuable theory and evidence for conservation ecology, biodiversity, habitat management, as well as the dynamics and stability of the ecosystem. Comparing with biological experiments, network methods based on topological structure possess particular advantage in the identification of keystone species. In present study, we quantified the relative importance of species in Carpinteria Salt Marsh food web by analyzing five centrality indices. The results showed that there were large differences in rankings species in terms of different centrality indices. Moreover, the correlation analysis of those centralities was studied in order to enhance the identifying ability of keystone species. The results showed that the combination of degree centrality and closeness centrality could better identify keystone species, and the keystone species in the CSM food web were identified as, Stictodora hancocki, small cyathocotylid, Pygidiopsoides spindalis, Phocitremoides ovale and Parorchis acanthus. Key words keystone species; topological parameters; centrality indices; biological networks. Network Biology ISSN 2220­8879 URL: http://www.iaees.org/publications/journals/nb/online­version.asp RSS: http://www.iaees.org/publications/journals/nb/rss.xml E­mail: [email protected] Editor­in­Chief: WenJun Zhang Publisher: International Academy of Ecology and Environmental Sciences 1 Introduction Food webs are complex ecological networks describing trophic relationships between species in a certain area (Pimm, 1982; Belgrano et al., 2005; Arii et al., 2007). If the entire food web is treated as a graph, the nodes in the graph represent different species (individuals) in the ecosystem and the edges denote the interactions between species (individuals). As a kind of network, food webs provide a new way to study communities (Albert and Barabasi, 2002; Newman, 2003). To some extent, such a network is a formalized description for complex relationships between species within the system. The concept of keystone species originated from the thought that species diversity of an ecosystem was controlled by the predators in the food chains, and they affected many other creatures in the ecosystem. IAEES www.iaees.org 14 Network Biology, 2015, 5(1): 13-33 Keystone species refer to those that biomass is disproportionate with its impact on the environment, and the extinction of keystone species may lead to the collapse of communities (Paine, 1969; Mills et al., 1993; Springer et al., 2003). The concept of keystone species means that an ecological community is not just a simple collection of species (Mouquet, 2013). As a result, the ecologically important species might not necessarily be the rare species conservation biologists always believed (Simberloff, 1998), because rare species are associated with the little biomass and abundance of species, and the importance of species is a kind of functional properties of the network. Therefore, the traditional protection pattern for rare species should be gradually transformed into the maintenance of keystone species (Wilson, 1987). Keystone species strongly affect species richness and ecosystem dynamics (Piraino et al., 2002), so the research of keystone species is an important area for predicting and maintaining the stability of ecosystem (Naeem and Li, 1997; Tilman, 2000). Definition of keystone species emphasizes the functional advantages of species in the ecosystem, and whether a species is a keystone species depends upon if it has a consistent effect in ecological function (Power et al., 1996), namely its sensitivity to environmental changes, such as competition, drought, floods and other ecological processes. In the past, researchers used many field experimental methods to study keystone species, but they mainly focused on the impact of changes in the abundance of a species on the other species (Paine, 1992; Wootton, 1994; Berlow, 1999). The main identification methods include control simulation method (Paine, 1995; Bai, 2011), equivalent advantage method (Khanina, 1998; Ji, 2002), competitive advantage method (Yeaton, 1988; Bond, 1989), the relative importance of species interactions method (Tanner and Hughes, 1994), community importance index method (Power et al., 1996), keystone index method (Jordán et al., 1999) and functional importance index method (Hurlbert, 1997). However, these methods mainly concentrated on a few species. Thus researchers need to do an assessment of the interactions between species in the community before the experiment, in order to determine species not important or interesting. So these methods are obvious subjective and produce certain mistake on identifying keystone species (Wootton 1994; Bustamante et al., 1995). Furthermore, monitoring species reaction to changes in the external environment through the above experimental methods requires that experimenters have a high professional quality. And because of the longer experimental time span, greater cost (Ernest and Brown, 2001), as well as other factors during the experiment, they are only suitable for semi-artificial or simple controllable ecosystems. It is more difficult to judge whether a species is a keystone species based on certain characteristics of species (Menge et al., 1994). So far, we don’t have a perfect and universally applicable method to identify keystone species. Research of keystone species has evolved from the initial direct experimental methods to network/software analysis. For example, Libralato et al. (2006) analyzed keystone indicators of functional groups of a species or a group of species in food web model through the ecosystem modeling (the Ecopath with Ecosim, EwE), and then ranked the level of the key indicators to obtain the keystone species. Jordán et al. (2008) pointed out that there were at least two methods to quantitatively assess the importance of species in communities. One was the structural importance of network analysis and another for the functional importance of network analysis. So they calculated the structural importance and the functional importance of species in the food web in Prince William Sound by CosBiLaB Graph software, and evaluated the advantages and disadvantages of the two methods. They believed that the combination of these two methods in the future would be the most important way to research dynamic mechanism. Kuang and Zhang (2011) analyzed the topological properties of the food web in Carpinteria Salt Marsh and found that parasites played a very important role in the food web, and the addition of parasites in the food web would change some properties and greatly increase the complexity of the food web. Therefore, the relationship between keystone species and topological characteristics can provide an effective method to understand and describe the topological structures, dynamic characteristics and the IAEES www.iaees.org Network Biology, 2015, 5(1): 13-33 15 complexity of functions between species within the food web. And it also can provide valuable theory and evidence for conservation ecology, biodiversity, habitat management, as well as the dynamics and stability of the ecosystem. Nevertheless, so far we lack of effective methods to identify keystone species and quantify their relative importance, so the quantitative assessment of species importance in the food web is becoming increasingly important and urgent (Paine, 1966; Power et al, 1996; Jordán, 2008). In recent years, there have been some major discoveries about the topological properties of complex systems (Strogatz, 2001; Albert and Barabási, 2002; Newman, 2003), and these also affect the definition and identification of keystone species. For example, the highly connected species were found to have more important influence on sustainability of food webs (Soulé and Simberloff, 1986), which promoted the generation of the concept of degree. Degree of nodes thus become the most widely used topological parameter to measure the keystone species (Dunne et al., 2002a). Degree refers to the direct impacts between species (Callaway et al., 2000; West, 2001; Zhang, 2011, 2012a, 2012b, 2012c, 2012d). However, indirect impacts between species are also important (Wooton, 1994; Huang, et al., 2008). For example, Darwin (1859) described the influence of cats on the clovers. Although indirect effects of chemical and behavioral studies may be difficult to quantify, some indirect impacts of network links have been proposed (Ulanowicz and Puccia, 1990; Patten, 1991). Thus the concept of centrality is proposed to address this problem. Centrality focuses on the indirect effects between species. The impacts of food webs are generally spread through indirect ways, so it may require detailed research and quantitative description on the effective range of indirect interactions from a specific point to the entire network (Jordán, 2001). In other words, it is necessary to determine how relevant these species are in the food web (Yodzis, 2000; Williams et al.,
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