Ecological Modelling 251 (2013) 271–278
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Ecological Modelling
jo ur n al homep ag e: www.elsevier.com/locate/ecolmodel
Effects of space partitioning in a plant species diversity model
Jinbao Liao
a,b,c
, Zhenqing Li
b,∗
, Jan J. Quets
a
, Ivan Nijs
a
a
Research Group Plant and Vegetation Ecology, Department of Biology, University of Antwerp (Campus Drie Eiken), Universiteitsplein 1, B-2610 Wilrijk, Belgium
b
State Key Laboratory of Vegetation and Environmental Change, Institute of Botany, Chinese Academy of Sciences, Beijing 100093, China
c
Graduate University of Chinese Academy of Sciences, Beijing 100049, China
a r t i c l e i n f o
Article history:
Received 27 July 2012
Received in revised form
23 November 2012
Accepted 28 December 2012
Available online 31 January 2013
Keywords:
Grid-based model
Spatially explicit model
Species coexistence
Species richness
Trait variation
Voronoi partitioning
a b s t r a c t
Understanding the mechanisms of species diversity maintenance within plant communities has become
a fundamental issue in ecology over the past decades. While some models have tried to explore these
mechanisms, few studies have integrated the dynamic interactions with neighbours in a spatially explicit
way. The present model uses Voronoi polygons to dynamically partition a landscape patch into areas
occupied by individual plants. It thus incorporates neighbourhood competition for space, unlike grid-
based models with nearest-neighbour competition. In closed two-species communities, dynamic Voronoi
partitioning promoted species coexistence, especially under local dispersal. This suggests that grid-based
models overestimate species extinction rates. Likewise, multispecies communities without immigration
had substantially greater species richness in the space partitioning model than in the grid-based model
but only under distance-limited dispersal. In contrast, richness levels were similar in both models under
global dispersal or with immigration from the metacommunity. Trait variation among species reduced
species richness, but more so for traits associated with competition for space. This suggests that some
traits are more important than others in governing species richness. Overall, our study demonstrates
that combining species identity (traits) with partitioning of physical space can improve understanding
of diversity regulation.
© 2013 Elsevier B.V. All rights reserved.
1. Introduction
A fundamental issue of ecology is to understand the forces that
maintain species diversity within communities (Hutchinson, 1959;
Levins, 1970; May, 1975; Pacala and Tilman, 1993; Chesson, 2000;
Hubbell, 2001). Two of the most influential theories are the niche
theory (Hutchinson, 1959) and the neutral theory (Hubbell, 2001).
The niche theory stresses a role for meaningful differences in the
niche of coexisting species (Weiher and Keddy, 1999; Wright,
2002; Chase and Leibold, 2003; Silvertown, 2004), which originate
from interspecific tradeoffs in the ability to exploit different
Abbreviations: A, actual area occupied by an individual resulting from Voronoi
partitioning;
¯
A, area need for a species in order not to be affected by density depend-
ent mortality; B, probability that an empty site is occupied by an individual; D, death
probability of an individual; L, length of a simulated patch; M, number of species in
a patch; n, number of neighbours for an individual; (ω), discriminant function that
represents the degree of competition between the target individual and its neigh-
bours; s, intrinsic seed production rate per individual of a species; m, density of
species m in the community; , seed influx rate at a given site; ˛, species sensitivity
to plant local density; , intrinsic (density-independent) mortality.
∗
Corresponding author at: 20 Nanxincun, Xiangshan, Haidian District, Beijing
100093, China. Tel.: +86 10 62836956; fax: +86 10 62836956.
E-mail addresses: jinbaoliao@ibcas.ac.cn (J. Liao), lizq@ibcas.ac.cn (Z. Li),
jan.quets@ua.ac.be (J.J. Quets), ivan.nijs@ua.ac.be (I. Nijs).
environments or resources (MacArthur and Levins, 1967; Levin,
1970; MacArthur, 1972; Tilman, 1982; Chesson, 2000). However,
in the light of niche theory, it remains unclear why competitive
exclusion does not occur when species compete for the same
resources for a very long time, and why hundreds of species with
very similar resource needs can coexist (May, 1990; Alonso and
Solé, 2000; Hubbell, 2001; Bell, 2000, 2001, 2003).
Given the problems with niche theory, the neutral model of bio-
diversity was developed (Bell, 2000, 2001; Hubbell, 2001), which
aimed to explain coexistence in diverse communities with dis-
persal and stochastic demographic processes. For its good fit to
empirical relative abundance curves (Hubbell, 2001; Gilbert et al.,
2006; Halley and Iwasa, 2011), the neutral biodiversity theory has
increasingly been applied in both theoretical and empirical stud-
ies (Volkov et al., 2005, 2007; Etienne et al., 2007; Chase, 2007;
Allouche and Kadmon, 2009). However, major controversies have
also arisen, in particular concerning the neutral assumption that
species have identical functional traits, which is obviously not the
case (Harte, 2003). Bell (2000, 2001) and Hubbell (2001), how-
ever, put forward that interspecific differences generally lead to
the existence of trade-offs that equalize overall fitness, and thus are
insufficient to affect community structure and species abundance.
Rather than continuing the controversy on which model pro-
vides a better explanation of species coexistence, further study
should unify the essence of both the niche and the neutral theory
0304-3800/$ – see front matter © 2013 Elsevier B.V. All rights reserved.
http://dx.doi.org/10.1016/j.ecolmodel.2012.12.030