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Limiting Similarity and Functional Diversity Along Environmental Gradients Ecology Letters, (2005) 8: 272–281 doi: 10.1111/j.1461-0248.2004.00720.x LETTER Limiting similarity and functional diversity along environmental gradients Abstract Dylan W. Schwilk1 and David D. Recent developments in community models emphasize the importance of incorporating Ackerly2* stochastic processes (e.g. ecological drift) in models of niche-structured community 1US Geological Survey, BRD/ assembly. We constructed a finite, spatially explicit, lottery model to simulate the WERC, Sequoia-Kings Canyon distribution of species in a one-dimensional landscape with an underlying gradient in Field Station, 47050 General environmental conditions. Our framework combines the potential for ecological drift Highway, Three Rivers, CA with environmentally-mediated competition for space in a heterogeneous environment. 93271, USA We examined the influence of niche breadth, dispersal distances, community size (total 2Department of Integrative number of individuals) and the breadth of the environmental gradient on levels of Biology, University of California, Berkeley, CA 94720, USA species and functional trait diversity (i.e. differences in niche optima). Three novel results *Correspondence: E-mail: emerge from this model: (1) niche differences between adjacent species (e.g. limiting [email protected] similarity) increase in smaller communities, because of the interaction of competitive effects and finite population sizes; (2) immigration from a regional species pool, stochasticity and niche-assembly generate a bimodal distribution of species residence times (ÔtransientÕ and ÔresidentÕ) under a heterogeneous environment; and (3) the magnitude of environmental heterogeneity has a U-shaped effect on diversity, because of shifts in species richness of resident vs. transient species. These predictions illustrate the potential importance of stochastic (although not necessarily neutral) processes in community assembly. Keywords Climate, community assembly, diversity, gradients, limiting similarity, neutral theory, stochasticity. Ecology Letters (2005) 8: 272–281 species, so they explicitly predict the maintenance of INTRODUCTION functional diversity (i.e. differences in resource use or niche The maintenance of diversity stands as one of the great parameters) in parallel with species diversity. theoretical (and empirical) challenges of ecology. The In contrast, non-niche-based models of diversity have principle of competitive exclusion states that two ecologic- examined the role of stochastic dynamics and intrinsic ally identical species cannot coexist indefinitely. Niche frequency-dependence, in the absence of explicit differ- theory provided the first solution to the coexistence ences in speciesÕ ecological parameters. Island biogeography problem, based on the differentiation in resource use theory was an early example of a non-niche-based theory among co-existing species and associated reduction in the (MacArthur & Wilson 1967). More recently, Hubbell (1979, intensity of interspecific competition (MacArthur & Levins 1997, 2001) has championed a neutral theory of diversity 1967; MacArthur 1970; Tilman 1980). A variety of other based on stochastic demographic dynamics in a large meta- models have been proposed that lead to maintenance of community landscape. In Hubbell’s neutral theory, speci- diversity, such as competition-colonization trade-offs, stor- ation in the regional species pool counteracts random age effects, and chaotic oscillations (Chesson & Warner demographic extinctions, and migration between communi- 1981; Tilman 1990; Pacala & Rees 1998; Huisman & ties maintains diversity in the face of random local Weissing 1999). A critical feature shared by all of these extirpation. The neutrality assumption is that all species are models is that the mechanisms of coexistence are based on demographically identical, and therefore species diversity is differences in demographic or ecological attributes of the maintained without any contribution of functional or Ó2005 Blackwell Publishing Ltd/CNRS Diversity and gradients 273 demographic diversity among species. This model has Our model combines the deterministic features of niche reinvigorated a long debate on the role of stochastic and differentiation models with the demographic stochasticity non-equilibrium processes in plant community ecology: and immigration from a regional species pool that charac- processes that can maintain species numbers with unstable terize Hubbell’s neutral model. The primary objectives of turnover of species identity and relative abundance (Loreau our model are twofold: first, we address the contribution of & Mouquet 1999; Bell 2000; Hubbell 2001; Chave et al. 2002; community size (number of individuals) to equilibrium Chave 2004). diversity levels. We hypothesize that demographic stochas- These contrasting models offer very different explana- ticity may provide a solution to the problem of limiting tions for diversity, and predictions regarding the factors that similarity in light of recent theoretical work (Hurtt & Pacala will influence diversity levels. The neutral theory explains 1995; Chesson 2000; Tilman 2004) and that realized niche diversity in terms of the balance of speciation/extinction in widths should increase, and diversity decrease, as commu- the meta-community and immigration/extirpation in the nity size decreases. Second, we explore a continuum of local community. The key attribute of individual commu- models from full neutrality to strong niche differentiation nities is their absolute size, in numbers of individuals J, and and examine the consequences for overall diversity and diversity is a monotonically increasing function of J. Total realized similarity. Environmental structure should provide population size has long been recognized as a key factor in Ôsafe sitesÕ for species and therefore increasing the breadth population biology and population genetics, where muta- of the environmental gradient should increase diversity at a tion and drift act as the diversity creating and culling given community size. The model is presented primarily processes analogous to speciation and extinction. Finite through simulations with an extensive exploration of the population sizes introduce demographic stochasticity and parameter space, coupled with analysis of the deterministic several recent patch-occupancy models have made progress invisibility criterion implicit in our simulations. in combining demographic stochasticity and niche theory (Amarasekare & Nisbet 2001; Mouquet & Loreau 2002; MODEL PRESENTATION Wang et al. 2002). Recent work has suggested that demographic stochasticity (ecological drift) can explain Our model consists of a one-dimensional lattice landscape limiting similarity and increase realized niche widths (Hurtt with a simple monotonic environmental gradient. Mono- & Pacala 1995; Tilman 2004). tonic gradients on small spatial scales may only be observed Environmental heterogeneity is often invoked as the in certain habitats (e.g. lake and ocean shores, vernal pools, explanation for coexistence when there is niche-differenti- steep elevation gradients). In complex models, it is critical to ation (Harner & Harper 1976; Grubb 1977; Chesson & start with simple patterns to be certain we understand the Warner 1981; Comins & Noble 1985). This view thus mechanisms driving the results. Additionally, our model acts explains higher diversity in terms of greater levels of as a microcosm for large scale patterns on latitudinal and environmental heterogeneity or a reduction in limiting climatic gradients. similarity (closer packing of species along niche axes). For Each cell on the lattice landscape can be inhabited by a discrete patches, several models have shown that species single plant. The total number of individuals in the local diversity cannot exceed patch diversity (Chesson & Warner community is J. An environmental function maps each 1981; Pacala & Tilman 1994; Mouquet & Loreau 2002). location on the landscape to a value of the environmental However, for continuous and stable environments, with condition, E (for notation see Table 1). The environmental infinite community size, there is no theoretical upper limit units are relative and arbitrary. For all results we present, on diversity, and limiting similarity can approach zero this environmental value (E) is a linear function of location (Abrams 1983, 1996; Chesson 2000). Pacala & Tilman on the landscape ranging from Emin ¼ 0 to a variable (1994) suggested several processes that avoid this infinite maximum, Erange: diversity scenario, including temporal heterogeneity in x environmental conditions. Unfortunately, much of the E ¼ E þ E ð1Þ x min J range debate over limiting similarity has been muddied by a failure to distinguish the theoretical problem of absolute In our model, unlike in resource-drawdown models limits to invasion of new species (Abrams 1996) from the (Chase & Leibold 2003), plants have no feedback effects on observed similarity of species that emerges under different the gradient. Individual death and recruitment follow the conceptual frameworks, i.e. Ôrealized limits to similarityÕ framework of Hurtt & Pacala (1995): sites are vacated by the (Pacala & Tilman 1994). We are concerned with the second random death of plants and vacant sites become occupied as problem in this paper, which we term Ôrealized similarityÕ, the result of competition among seedlings. which is expressed as the mean distance between species Species (and their constituent individuals) have two traits, niche
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