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5 results for “dytiscid”
Figure 4 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 4 Stations in which Graphoderusbilineatus (yellow), G.cinereus (red) and G.zonatus (blue) were captured: A) in the Motte reserve and B) in the Ostende reserve in 2018. The dotted lines represent the reserve boundaries and the grey points the sampled stations in which no Graphoderus were captured. Background picture obtained from the Swiss Federal Office of Topography swisstopo.
Figure 3 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 3 Stations in which Graphoderusbilineatus was captured in the Motte reserve in 2014 (green) and in 2018 (yellow). The dotted lines represent the reserve boundaries and the grey points the sampled stations (2018) in which no Graphoderusbilineatus were captured. Background picture obtained from the Swiss Federal Office of Topography swisstopo.
Figure 1 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 1 Graphoderusbilineatus. Copyright: Yerpo [CC BY-SA 4.0 (https://creativecommons.org/licenses/by-sa/4.0)], from Wikimedia Commons.
Figure 5 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 5 Principal component (PC) for habitat depth, helophyte cover and hydrophyte cover for G.bilineatus (green) and G.cinereus (blue). The first principal component (PC1) explains 59% of the variance. The first two components (PC1 and PC2) explain 81% of the total variance. While factor loads of habitat depth, helophyte cover and hydrophyte cover for PC1 are similar, helophyte cover and depth strongly negatively influence PC2. Circles represent 95% probability ellipses.
Figure 2 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 2 Location of the sampling stations in the Grande Cariçaie nature reserves, on the south eastern shore of Lake Neuchâtel. We sampled seven reserves in 2018 (delimited in brown polygons): 1) Grèves de Cheseaux, 2) Baie d'Yvonand, 3) Cheyres, 4) Grèves de la Corbière et de Chevroux, 5) Grèves d'Ostende et de Chevroux, 6) Grèves de la Motte and 7) Cudrefin. The orange points represent the sampled stations (N = 101 stations). Background picture obtained from the Swiss Federal Office of Topography swisstopo.
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