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Population demography of alpine butterflies: Boloria pales and Boloria napaea (Lepidoptera: Nymphalidae) and their specific adaptations to high mountain environments
Affiliation:1. Biogeography, Trier University, D-54286 Trier, Germany;2. Haus der Natur Salzburg, A-5020 Salzburg, Austria;3. Senckenberg German Entomological Institute, D-15374 Müncheberg, Germany;4. Entomology, Department of Zoology, Institute of Biology, Martin Luther University Halle-Wittenberg, D-06099 Halle (Saale), Germany;1. Unidad de Recursos Naturales, Centro de Investigación Científica de Yucatán, A. C., Calle 43 Núm. 130, Colonia Chuburná de Hidalgo, Mérida, 97205, Yucatán, Mexico;2. Instituto de Ecología Aplicada, Universidad Autónoma de Tamaulipas, Avenida División del Golfo Núm. 356, Colonia Libertad, Ciudad Victoria, 87019, Tamaulipas, Mexico;3. Functional Ecology Group, Institute of Biology and Environmental Sciences, University of Oldenburg, Box 2503, 26111 Oldenburg, Germany;1. Zhejiang Provincial Key Laboratory of Plant Evolutionary Ecology and Conservation, Taizhou University, Taizhou 318000, Zhejiang Province, China;2. School of Nature Conservation, Beijing Forestry University, Beijing 100083, China;1. Department of Botany, Faculty of Science, University of South Bohemia, Branišovská 1760, 370 05 České Budějovice, Czech Republic;2. Institute of Entomology, Biology Centre of the Academy of Sciences of the Czech Republic, Branišovská 31, 370 05 České Budějovice, Czech Republic;1. Institute of Biochemistry and Biology, General Botany, University of Potsdam, Maulbeerallee 3, 14469 Potsdam, Germany;2. Department of Biodiversity and Landscape Ecology, Faculty of Biology and Chemistry, Osnabrück University, Barbarastraße 13, 49076 Osnabrück, Germany;3. Institute of Biodiversity and Landscape Ecology (IBL), Hafenweg 31, 48155 Münster, Germany;1. UR SPHERES, Behavioural Biology Unit, Université de Liège, Quai van Beneden 22, Liège, Belgium;2. UMR 7179 MECADEV CNRS-MNHN, Département Ecologie et Gestion de la Biodiversité, Muséum National d’Histoire Naturelle, Brunoy, France;3. TERRA Research Center, Central African Forests, Gembloux Agro-Bio Tech, Université de Liège, Belgium;4. Nature Forest Environment, Freelance in Tropical Forestry, Belgium;1. Departamento de Ciências Biológicas, Universidade Federal dos Vales do Jequitinhonha e Mucuri, Rodovia MGT 367-Km 583, nº 5000, Alto da Jacuba, CEP 39100-000, Diamantina, MG, Brazil;2. Departamento de Engenharia Florestal, Universidade Federal dos Vales do Jequitinhonha e Mucuri, Rodovia MGT 367-Km 583, nº 5000, Alto da Jacuba, CEP 39100-000, Diamantina, MG, Brazil;3. Departamento de Geografia, Universidade Federal dos Vales do Jequitinhonha e Mucuri, Rodovia MGT 367-Km 583, nº 5000, Alto da Jacuba, CEP 39100-000, Diamantina, MG, Brazil
Abstract:High mountain ecosystems are extreme habitats, and adaptation strategies to this ecosystem are still poorly understood in most groups. To unravel such strategies, we performed a MRR study in the Hohe Tauern National Park (Salzburg, Austria) with two nymphalid butterfly species, Boloria pales and B. napaea. We analysed their population structure over one flight period by studying the development of population size and wing wear. B. pales had more individuals and a higher survival probability than B. napaea; the sensitivity to extreme weather conditions or other external influences was higher in B. napaea. We only observed proterandry in B. pales. Imagines of both species survived under snow for at least some days. Additionally, we observed a kind of risk-spreading, in that individuals of both species, and especially B. pales, have regularly emerged throughout the flight period. This emergence pattern divided the population's age structure into three phases: an initial phase with decreasing wing quality (emergence > mortality), followed by an equilibrium phase with mostly constant average wing condition (emergence = mortality) and a final ageing phase with strongly deteriorating wing condition (mortality » emergence). Consequently, neither species would likely become extinct because of particularly unsuitable weather conditions during a single flight period. The observed differences between the two species suggest a better regional adaptation of B. pales, which is restricted to high mountain systems of Europe. In contrast, the arctic-alpine B. napaea might be best adapted to conditions in the Arctic and not the more southern high mountain systems. However, this needs to be examined during future research in the Arctic.
Keywords:High alpine butterflies  Age structure  Ecological adaptation  Population ecology  Proterandry  Risk-spreading
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