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712 results for “Beetle diversity”
Figures 15-21 from: Konstantinov A, Konstantinova A (2011) New genus and species of flea beetles (Coleoptera, Chrysomelidae, Galerucinae, Alticini) from Puerto Rico, with comments on flea beetle diversity in the West Indies and a key to the West Indian Monoplatini genera. ZooKeys 155: 61-87. https://doi.org/10.3897/zookeys.155.2124
Figures 15-21 - Distigmoptera chamorrae: 15 habitus, dorsal view, male 16 habitus, frontalview, female 17 habitus, lateral view, male 18 habitus, dorsal view, female 19 metatibia and metatarsus, lateral view 20 claw, male 21 claw, female.
Figures 47-50 from: Konstantinov A, Konstantinova A (2011) New genus and species of flea beetles (Coleoptera, Chrysomelidae, Galerucinae, Alticini) from Puerto Rico, with comments on flea beetle diversity in the West Indies and a key to the West Indian Monoplatini genera. ZooKeys 155: 61-87. https://doi.org/10.3897/zookeys.155.2124
Figures 47-50 - Ulrica eltoro: 47 habitus, dorsal view 48 habitus, frontalview 49 habitus, lateral view 50 median lobe of aedeagus, ventral, lateral and dorsal views.
Figures 28-34 from: Konstantinov A, Konstantinova A (2011) New genus and species of flea beetles (Coleoptera, Chrysomelidae, Galerucinae, Alticini) from Puerto Rico, with comments on flea beetle diversity in the West Indies and a key to the West Indian Monoplatini genera. ZooKeys 155: 61-87. https://doi.org/10.3897/zookeys.155.2124
Figures 28-34 - Kiskeya elyunque: 28 habitus, frontalview 29 habitus, lateral view 30 labium and maxilla 31 labrum 32 last seven antennomeres 33 mandible 34 metendosternite.
Figure 3 from: Šerić Jelaska L, Dumbovich V, Kucinic M (2011) Carabid beetle diversity and mean individual biomass in beech forests of various ages. ZooKeys 100: 393-405. https://doi.org/10.3897/zookeys.100.1536
Figure 3 - Proportion of species according to their hibernation strategies (larvae – black columns, adults – white columns) in relation to forest age (years).
Figure 3 from: Schuldt A, Assmann T (2011) Belowground carabid beetle diversity in the western Palaearctic – effects of history and climate on range-restricted taxa (Coleoptera, Carabidae). ZooKeys 100: 461-474. https://doi.org/10.3897/zookeys.100.1540
Figure 3 - Partitioning of variation from regression modelling for species richness of belowground carabids. Values give the % of the total variation independent and shared effects of spatial (S), topographic (T) and climate (C) models account for in the explanation of richness patterns. U is the unexplained variation.
Figure 2 from: Schuldt A, Assmann T (2011) Belowground carabid beetle diversity in the western Palaearctic – effects of history and climate on range-restricted taxa (Coleoptera, Carabidae). ZooKeys 100: 461-474. https://doi.org/10.3897/zookeys.100.1540
Figure 2 - Relationship between species richness of belowground carabid beetles (log10-transformed) and a latitude (R²adj.=0.51; p=0.012), b range in elevation (i.e., topograohic variability; R²adj.=0.52; p<0.001) and c annual potential evapotranspiration (R²adj.=0.38; p=0.020) in the western Palaearctic.
Figure 1 from: Schuldt A, Assmann T (2011) Belowground carabid beetle diversity in the western Palaearctic – effects of history and climate on range-restricted taxa (Coleoptera, Carabidae). ZooKeys 100: 461-474. https://doi.org/10.3897/zookeys.100.1540
Figure 1 - Distribution of species richness of belowground carabid beetles across the western Palaearctic, based on Löbl and Smetana (2003). Shadings and symbols indicate the number of species recorded for each country. Countries with 11–20 subterranean species are marked by a filled circle, countries with 1–10 species by an open circle. Countries for which no subterranean species have been recorded are white and without a symbol.
Figure 1 from: Davidson R, Ryyken J, Farrell B (2011) Carabid beetle diversity and distribution in Boston Harbor Islands national park area (Coleoptera, Carabidae). ZooKeys 147: 497-526. https://doi.org/10.3897/zookeys.147.2111
Figure 1 - Figure 1. Location of Boston Harbor Islands national park area. Islands/peninsulas sampled for carabid beetles are shaded in black.
Figure 2 from: Davidson R, Ryyken J, Farrell B (2011) Carabid beetle diversity and distribution in Boston Harbor Islands national park area (Coleoptera, Carabidae). ZooKeys 147: 497-526. https://doi.org/10.3897/zookeys.147.2111
Figure 2 - Figure 2. Relationship between island area and species richness of carabid beetles in Boston Harbor Islands national park area. Value for species richness has been standardized across all islands to include only one full season of sampling.
Figure 5 from: Riley K, Browne R (2011) Changes in ground beetle diversity and community composition in age structured forests (Coleoptera, Carabidae). ZooKeys 147: 601-621. https://doi.org/10.3897/zookeys.147.2102
Figure 5 - Relative abundance across the forest age gradient for a representative species from each of the indicator classes (see text for definitions of indicator classes).
Figure 4 from: Riley K, Browne R (2011) Changes in ground beetle diversity and community composition in age structured forests (Coleoptera, Carabidae). ZooKeys 147: 601-621. https://doi.org/10.3897/zookeys.147.2102
Figure 4 - Proportions of carabid populations brachypterous and macropterous for five forest age classes. Significant differences occurred for all forest age classes except the zero age class (χ2 < 0.05).
Figure 3 from: Riley K, Browne R (2011) Changes in ground beetle diversity and community composition in age structured forests (Coleoptera, Carabidae). ZooKeys 147: 601-621. https://doi.org/10.3897/zookeys.147.2102
Figure 3 - Results of Non-Metric Multidimensional Scaling (NMDS) analysis for 33 study sites. The analysis was based on the 17 most common carabid beetle species from five forest age classes (0, 10, 50, 85, and 150 years). Each the five polygons represent different forest age classes, as indicated by different symbols.
Figure 2 from: Riley K, Browne R (2011) Changes in ground beetle diversity and community composition in age structured forests (Coleoptera, Carabidae). ZooKeys 147: 601-621. https://doi.org/10.3897/zookeys.147.2102
Figure 2 - Carabid beetle species accumulation curves for five forest age classes. Vertical line indicates species richness of each curve at n = 233 individuals.
Figure 4 from: Šerić Jelaska L, Dumbovich V, Kucinic M (2011) Carabid beetle diversity and mean individual biomass in beech forests of various ages. ZooKeys 100: 393-405. https://doi.org/10.3897/zookeys.100.1536
Figure 4 - Dendrogram of cluster analyses among forest sites using presence/absence carabid beetle data. Two distinct clusters are formed at roughly 30% similarity. Marks 60y 1–3, 80y 1–3 and 150y. 1–3 denote investigated sites placed in the 60-, 80- and 150-year-old forests.
Figure 1 from: Šerić Jelaska L, Dumbovich V, Kucinic M (2011) Carabid beetle diversity and mean individual biomass in beech forests of various ages. ZooKeys 100: 393-405. https://doi.org/10.3897/zookeys.100.1536
Figure 1 - Position of investigated sites labelled according to the age of the forest ("60y 1–3" denote sites 1 to 3 in the 60-year-old forest, "80y 1–3" denote sites 1 to 3 in the 80-year-old forest and "150y 1–3" denote sites 1 to 3 in the 150-year-old forest). Insert: location of Papuk Nature Park in Croatia.
Figure 6 from: Rodríguez-Flores PC, Gutiérrez-Rodríguez J, Aguirre-Ruiz EF, García-París M (2016) Salt lakes of La Mancha (Central Spain): A hot spot for tiger beetle (Carabidae, Cicindelinae) species diversity. ZooKeys 561: 63-103. https://doi.org/10.3897/zookeys.561.6042
Figure 6 - Representative habitats of Cicindelinae in La Mancha. A Channel at Laguna de las Yeguas (Ciudad Real) in May. Wet areas occupied by Calomera littoralis littoralis and Cicindela campestris; when drier, occupied by Cephalota maura maura B Road side pools and halophytic vegetation in Laguna de Manjavacas (Cuenca) in April. Calomera littoralis littoralis was the only species observed C Wells and deep pools in Laguna de Manjavacas (Cuenca) in June. Cephalota maura maura is frequent in these structures D Laguna del Pueblo de Pedro Muñoz (Ciudad Real) in July. Mud areas amongst hydrophytic matts, occupied by Calomera littoralis littoralis and Myriochila melancholica melancholica E Temporary pools at Laguna del Longar (Toledo), in July. Calomera littoralis littoralis, Myriochila melancholica melancholica and Cephalota maura co-occcur at the sides F Laguna del Taray Chico (Cuenca) in May. Trails and non-halophytic prairies near the fresh water lake, occupied by Cicindela campestris campestris. Photographs by N. Percino and MG-P.
Figure 11 from: Rodríguez-Flores PC, Gutiérrez-Rodríguez J, Aguirre-Ruiz EF, García-París M (2016) Salt lakes of La Mancha (Central Spain): A hot spot for tiger beetle (Carabidae, Cicindelinae) species diversity. ZooKeys 561: 63-103. https://doi.org/10.3897/zookeys.561.6042
Figure 11 - Characteristic habitat of the La Mancha endemic tiger-beetle Cephalota (Taenidia) dulcinea. A Trails at laguna del Taray (Toledo) B Trails and halophytic vegetation in Laguna de Pajares (Ciudad Real), where it was found in company of Cephalota maura maura C Trails and "albardinal" in Laguna del Altillo Chica (Toledo), where it co–occurs with Cylindera paludosa D Open areas amongst halophytic vegetation at laguna de La Sal (Toledo), Calomera littoralis littoralis and Cicindela maroccana occur in this habitat at the end of the spring E Halophytic vegetation at Laguna de Peña Hueca (Toledo), in this spot, Calomera littoralis littoralis and Cicindela maroccana are present at the end of the spring F Halophytic vegetation and open areas with salty granulated soils at Laguna de Sánchez Gómez (Cuenca). Photographs MG-P.
Figure 14 from: Rodríguez-Flores PC, Gutiérrez-Rodríguez J, Aguirre-Ruiz EF, García-París M (2016) Salt lakes of La Mancha (Central Spain): A hot spot for tiger beetle (Carabidae, Cicindelinae) species diversity. ZooKeys 561: 63-103. https://doi.org/10.3897/zookeys.561.6042
Figure 14 - Location of seven species of Cicindelinae at Laguna del Longar (Lillo, Toledo). Colour dots indicate the spatial position of each specimen (often, more than one specimen are presented under a single dot) (see legend). Note the spatial segregation of most species. Dots in lower right area, where Myriochila melancholica melancholica was found, correspond to the habitat shown in Fig. 6e. Dots in the upper left area, where Cicindela campestris campestris was present, correspond to the habitat shown in Fig. 13c.
Figure 5 from: Rodríguez-Flores PC, Gutiérrez-Rodríguez J, Aguirre-Ruiz EF, García-París M (2016) Salt lakes of La Mancha (Central Spain): A hot spot for tiger beetle (Carabidae, Cicindelinae) species diversity. ZooKeys 561: 63-103. https://doi.org/10.3897/zookeys.561.6042
Figure 5 - Representative habitats of Cicindelinae in La Mancha. A Laguna de la Sal (Toledo) in May. Salt flats occupied by Calomera littoralis littoralis B Laguna de Peña Hueca (Toledo) in April. Wet salt flats, with gypsum outcrops, occupied by Calomera littoralis littoralis; when totally dry, in summer, occupied by Cephalota circumdata imperialis C Laguna de Las Yeguas (Ciudad Real) in June. Salt flats, occupied by Calomera littoralis littoralis and Cephalota circumdata imperialis; and halophytic prairies occupied by Cephalota dulcinea and Cylindera paludosa D La Laguna de Miguel Esteban (Toledo) in July. Salt flats, occupied by Calomera littoralis littoralis; and halophytic prairies with "albardinal" occupied by Cephalota maura maura E Laguna del Camino de Villafranca (Ciudad Real), with flamingos, in July. Sapropel shores occupied by Calomera littoralis littoralis F Laguna de Alcahozo (Ciudad Real) in June. Salt flats, occupied by Calomera littoralis littoralis and Cephalota circumdata imperialis; and open areas near dry halophytic prairies occupied by Cephalota dulcinea and also by Cephalota circumdata imperialis. Photographs by N. Percino and MG-P.
Figure 9 from: Rodríguez-Flores PC, Gutiérrez-Rodríguez J, Aguirre-Ruiz EF, García-París M (2016) Salt lakes of La Mancha (Central Spain): A hot spot for tiger beetle (Carabidae, Cicindelinae) species diversity. ZooKeys 561: 63-103. https://doi.org/10.3897/zookeys.561.6042
Figure 9 - Frequency of observation of Cicindelinae during the sampling period (April to August), all sites pooled. From top to bottom: Cephalota circumdata imperialis, Cephalota dulcinea, and Cylindera paludosa.
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