From metapopulation theory to conservation recommendations: Lessons from spatial occurrence and abundance patterns of Maculinea butterflies
Introduction
With many species living nowadays in increasingly fragmented landscapes metapopulation theory has become a paradigm in biodiversity conservation (Hanski and Gaggiotti, 2004). In its classic form, exemplified by Levins’ (1970) model or Hanski’s (1994) incidence function model, this theory assumes high frequency of extinction and colonisation events in local habitat patches. Consequently its main interest is focused on spatial presence–absence patterns rather than on abundance patterns. Only recently there have been attempts to incorporate local population sizes and their dynamics into metapopulation models (Keeling, 2002, Ovaskainen and Hanski, 2004). On the other hand, many authors have argued that classic metapopulations are in fact rare in the real world (Harrison and Taylor, 1997, Szacki, 1999, Smith and Green, 2005). Butterflies are believed to be one of the groups that best fit the theoretical framework of the classic metapopulation theory, but even among them there are exceptions (Thomas and Hanski, 1997, Thomas and Hanski, 2004, Baguette, 2004).
Large Blue butterflies of the genus Maculinea, which over the last two decades have become the ‘flagships’ of biodiversity conservation in Europe (Thomas and Settele, 2004), obviously experience severe fragmentation of their habitats (Munguira and Martin, 1999). Nevertheless, based on their biology one may expect Maculinea not to be particularly prone to exist in classic metapopulations. They are characterised by unique life cycles requiring specific foodplants and host ants in the larval period (Elmes and Thomas, 1992, Thomas, 1995). Due to high density-dependant mortality experienced by larvae (Hochberg et al., 1992, Hochberg et al., 1994) populations of Maculinea are typically small, but remarkably demographically stable (Thomas et al., 1998a, Nowicki et al., 2005a, Nowicki et al., 2005b). Apart from this, mobility of Maculinea is very low compared to most other butterflies (Nowicki et al., 2005b, Nowicki et al., 2005c). Both features reduce the turnover of local populations and thus should increase the importance of their sizes and dynamics for the functioning of metapopulations.
The aim of the present study was to test (i) how well in reality Maculinea butterflies conform to the classic metapopulation theory, and (ii) which factors affect their occurrence and abundance patterns. Identifying such factors is per se crucial for Maculinea conservation, but it is also important to know whether the probability of occupancy of local habitat patches and population densities on them are determined by the same or different habitat parameters. The former situation would allow monitoring the success of conservation activities with presence–absence data, which are much easier to obtain than abundance estimates. It would also make possible to apply relatively simple classic metapopulation models, e.g. for testing future management scenarios. The opposite situation, in which occupancy probabilities and population densities are shaped by different habitat parameters, would obviously be less desirable for conservation, because it may involve conflicting management recommendations and the need to choose between different priorities, e.g. high occupancy rates vs. high local densities. To achieve our goals we surveyed occurrence and local densities of M. teleius, M. nausithous, and M. alcon on habitat patches in the Kraków region, southern Poland, where the three species live sympatrically in very large (except for M. alcon) metapopulations (Nowicki et al., 2005c, Nowicki et al., 2005d). Subsequently we analysed this information against a wide range of habitat parameters derived from a GIS analysis. In particular we were interested in assessing the relative importance of factors reflecting habitat quality of Maculinea foodplant patches versus spatial characteristics of these patches.
Section snippets
Study area
The study area comprised ca. 35 km2 wet meadow complex located in the Vistula river valley (50°01′ N; 19°54′ E) at an altitude of 200-240 m above sea-level. The meadows have been mostly abandoned for almost two decades and only a small fraction (ca. 5%) of their area is still mown annually in late spring. They include 61 patches of Sanguisorba officinalis (Fig. 1) – the foodplant of M. teleius and M. nausithous (Thomas, 1984, Thomas et al., 1998a) – with the total area of ca. 211 ha (range:
Results
In 2003 M. teleius could be observed on every single S. officinalis patch in the region, but in the following year there were four patches without the species. M. nausithous was in turn absent from 10 patches in 2003, and it apparently managed to (re)colonise 7 of them by 2004. M. alcon occupied the same 14 G. pneumonanthe patches in both years of the study (Table 2). The total metapopulation size of M. teleius was estimated at almost 150 thousand individuals in 2003 and about two thirds of
Structure of Maculinea metapopulations
Hanski (1999) described several characteristics of classic metapopulations, which can be summarised as follows: (1) breeding populations occupy discrete habitat patches; (2) the isolation of patches is not severe enough to prevent (re)colonisations of empty ones; (3) dynamics of local population are asynchronous, at least to the extent precluding simultaneous extinction of all of them; (4) none of the populations is large enough to be free from the risk of stochastic extinction; (5) a
Acknowledgements
We express our gratitude to Anna Amirowicz, Gabriela Krzywdzik, Balbina Kudlek, Dawid Moron, Artur Osikowski, Ewa Sliwinska, Hajnalka Szentgyörgyi, Aleksandra Walczynska, Marta Wantuch, and Kajetan Woyciechowski for their assistance in the fieldwork. Hans-Joachim Poethke, Thomas Hovestadt, David Nash, Thomas O. Crist, and three anonymous referees provided valuable comments on earlier versions of the manuscript. The study has been funded by the EC within its projects MacMan (EVK2-CT-2001-00126)
References (55)
The classical metapopulation theory and the real, natural world: a critical appraisal
Basic and Applied Ecology
(2004)- et al.
When is a habitat not a habitat? Dramatic resource use changes under differing weather conditions for the butterfly Plebejus argus
Biological Conservation
(2006) - et al.
Consequences of the spatial configuration of resources for the distribution and dynamics of the endangered Parnassius apollo butterfly
Biological Conservation
(2006) - et al.
Empirical evidence for metapopulation dynamics
- et al.
Functional conservation units for the endangered Alcon Blue butterfly Maculinea alcon in Belgium (Lepidoptera: Lycaenidae)
Biological Conservation
(2004) - et al.
An empirical evaluation of the area and isolation paradigm of metapopulation dynamics
Biological Conservation
(2007) - et al.
Butterfly metapopulations
- et al.
Metapopulation dynamics in changing environments: butterfly responses to habitat climate change
The behaviour and habitat requirements of Maculinea nausithous (the Dusky Large Blue) and M. teleius (the Scarce Large Blue) in France
Biological Conservation
(1984)- et al.
The role of ants in conservation monitoring: If, when, and how
Biological Conservation
(2006)
The evolution of alternative parasitic life histories in large blue butterflies
Nature
Zt: a software tool for simple and partial Mantel tests
Journal of Statistical Software
Towards a functional resource-based concept for habitat: a butterfly biology viewpoint
Oikos
Habitats and resources: the need for a resource-based definition to conserve butterflies
Biodiversity and Conservation
Empirical tests of specific predictions made from a spatial model of the population dynamics of Maculinea rebeli, a parasitic butterfly of red ant colonies
Acta Oecologica
The ecology of Myrmica ants in relation to the conservation of Maculinea butterflies
Journal of Insect Conservation
The complexity of species conservation: interactions between Maculinea butterflies and their ant hosts
Biodiversity and Conservation
New information on the biology Maculinea nausithous and M. teleius (Lepidoptera: Lycaenidae)
Nota Lepidoptera
Subdivision of nature reserves and the maintenance of species diversity
Nature
Patch area, population density and the scaling of migration mates: the resource concentration hypothesis revisited
Ecology Letters
A practical model of metapopulation dynamics
Journal of Animal Ecology
Metapopulation Ecology
Metapopulation structure and migration in the butterfly Melitaea cinxia
Ecology
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