Pollination ecology of a plant in its native and introduced areas |
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Affiliation: | 1. Estación Biológica de Doñana (EBD-CSIC), Avda. Américo Vespucio s/n, Isla de la Cartuja, 41092 Sevilla, Spain;2. Grupo de Investigación “Transferencia de I+D en el Área de Recursos Naturales”, Universidad de Almería, Ctra. de Sacramento s/n, 04120 La Cañada (Almería), Spain;1. Key Laboratory of Aquatic Botany and Watershed Ecology, Wuhan Botanical Garden, Chinese Academy of Sciences, Wuhan 430074, China;2. Guangxi Institute of Botany, Chinese Academy of Sciences, Guilin 541006, China;1. CoRFiLaC, Regione Siciliana, s.p. 25 km 5 Ragusa Mare, 97100 Ragusa, Italy;2. DISPA, University of Catania, via Val di Savoia 5, 95123 Catania, Italy;1. Programa de Pós-Graduação em Ecologia e Evolução, Instituto de Ciências Biológicas, Universidade Federal de Goiás, Caixa Postal 131, CEP 74001-970 Goiânia, Goiás, Brazil;2. Programa de Pós-Graduação em Ecologia, Instituto de Ciências Biológicas, Universidade de Brasília, Campus Universitário Darcy Ribeiro, Bloco E, Asa Norte, CEP 770910-900 Brasília, DF, Brazil;3. Programa de Pós-Graduação em Ciências Ambientais, Instituto de Ciências Biológicas, Universidade Federal de Goiás, Caixa Postal 131, CEP 74001-970, Goiânia, Goiás, Brazil;4. Departamento de Ecologia, Instituto de Ciências Biológicas, Universidade Federal de Goiás, Caixa Postal 131, CEP 74001-970 Goiânia, Goiás, Brazil;5. Laboratório de Macroecologia, Universidade Federal de Goiás, Campus II, BR 364, Km 192, CEP 75801-615 Jataí, Goiás, Brazil;1. Senckenberg Biodiversity and Climate Research Centre (BiK-F), Senckenberganlage 25, 60325 Frankfurt am Main, Germany;2. Department of Conservation Biology and Entomology and Centre for Invasion Biology, Stellenbosch University, Private Bag X1, Matieland 7602, South Africa;3. Institute of Landscape and Plant Ecology, University of Hohenheim, August-von-Hartmann-Str. 3, 70599 Stuttgart, Germany;4. Institut des Sciences de l’Evolution, UMR 5554, Université Montpellier 2, Place Eugène Bataillon, F-34095 Montpellier Cedex 05, France;5. Department of Botany and Zoology, Stellenbosch University, Private Bag X1, Matieland 7602, South Africa;6. Department of Biological Sciences, Johann Wolfgang Goethe-University, Max-von-Laue-Straße 9, 60438 Frankfurt am Main, Germany;1. Game and Wildlife Conservation Trust, Fordingbridge SP6 1EF, United Kingdom;2. Agroecology and Environment, Agroscope, CH-8046 Zurich, Switzerland;3. University of Koblenz-Landau, iES Landau, Institute for Environmental Sciences, Fortstr. 7, D-76829 Landau, Germany;4. Estonian University of Life Sciences, Kreutzwaldi 1, 51006 Tartu, Estonia;5. Institute of Life Sciences, Scuola Superiore Sant’Anna, 56127 Pisa, Italy;6. Plant Protection Institute, Szent Istvan University, H-2100 Godollo, Hungary;7. Wageningen University & Research, Wageningen Plant Research, Lingewal 1, 6668LA Randwijk, the Netherlands;8. Wageningen University & Research, Crop Systems Analysis, Droevendaalsesteeg 1, 6708PB Wageningen, The Netherlands;9. Biosciences, University of Exeter, Exeter EX4 4PS, United Kingdom;1. Laboratory of Biogeography & Ecology, Department of Geography, University of the Aegean, 81100 Mytilene, Greece;2. Department of Environmental and Natural Resources Management, University of Patras, 30100 Agrinio, Greece;3. Department of Ecology, School of Biology, Aristotle University, 54124 Thessaloniki, Greece;4. School of Natural Resources and the Environment, University of Arizona, Tucson, AZ 85718, USA |
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Abstract: | Entomophilous and obligate out-crossing non-native plants need to become well integrated in the resident plant–pollinator network to set seeds and become established. However, it is largely unknown how pollination patterns differ between native ranges and those where plants have been introduced.We compared the identity, abundance and visitation rates of pollinators, insect pollen loads, pollen deposition on stigmas, and fruit and seed sets of Hedysarum coronarium, an entomophilous short lived N-fixing perennial, in populations from native and introduced ranges in Spain (South of mainland Spain and Menorca Island, respectively).In both areas, Hedysarum was visited by a similar number of species, mainly hymenopterans; seven species were common between native and introduced areas. However, pollinator richness, abundance, and visits per flower were greater in the native than in the introduced range, as were fruit and seed sets. Hedysarum pollen loads on stigmas and on Apis mellifera, the most common pollinator, did not differ between areas. Lower abundance of pollinators might be causing lower visitation rates, and to some extent reducing Hedysarum fruit and seed sets in the introduced area.Our biogeographical approach shows that integration of a non-native plant in a resident pollinator network does not prevent pollen limitation in the introduced area. Therefore, despite being necessary, pollination mutualistic relationships might not be the key for non-native plant establishment success in the introduced area. |
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Keywords: | Biogeography Biological invasions Fruit set Mutualistic interactions Pollen deposition Pollinators |
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