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558 results for “dry forest”
Figure 5 from: Ariza GM, Jácome J, Esquivel HE, Kotze DJ (2021) Early successional dynamics of ground beetles (Coleoptera, Carabidae) in the tropical dry forest ecosystem in Colombia. In: Spence J, Casale A, Assmann T, Liebherr JК, Penev L (Eds) Systematic Zoology and Biodiversity Science: A tribute to Terry Erwin (1940-2020). ZooKeys 1044: 877-906. https://doi.org/10.3897/zookeys.1044.59475
Figure 5 Generalized Linear Mixed Model predicted (mean ± SE) number of individuals of Calosoma alternans, genus Megacephala and the remaining carabid beetle species collected from Armero and Cambao combined across the three habitat types (forest, early succession, and pasture). Note different y-axis scales.
Supplementary material 1 from: Ariza GM, Jácome J, Esquivel HE, Kotze DJ (2021) Early successional dynamics of ground beetles (Coleoptera, Carabidae) in the tropical dry forest ecosystem in Colombia. In: Spence J, Casale A, Assmann T, Liebherr JК, Penev L (Eds) Systematic Zoology and Biodiversity Science: A tribute to Terry Erwin (1940-2020). ZooKeys 1044: 877-906. https://doi.org/10.3897/zookeys.1044.59475
Table S1
Figure 4 from: Ariza GM, Jácome J, Esquivel HE, Kotze DJ (2021) Early successional dynamics of ground beetles (Coleoptera, Carabidae) in the tropical dry forest ecosystem in Colombia. In: Spence J, Casale A, Assmann T, Liebherr JК, Penev L (Eds) Systematic Zoology and Biodiversity Science: A tribute to Terry Erwin (1940-2020). ZooKeys 1044: 877-906. https://doi.org/10.3897/zookeys.1044.59475
Figure 4 Generalized Linear Model predicted (mean ± SE) number of individuals of Calosoma alternans and the remaining carabid beetle species collected from Armero across the three habitat types (forest, early succession, and pasture). Note different y-axis scales.
Figure 2 from: Ariza GM, Jácome J, Esquivel HE, Kotze DJ (2021) Early successional dynamics of ground beetles (Coleoptera, Carabidae) in the tropical dry forest ecosystem in Colombia. In: Spence J, Casale A, Assmann T, Liebherr JК, Penev L (Eds) Systematic Zoology and Biodiversity Science: A tribute to Terry Erwin (1940-2020). ZooKeys 1044: 877-906. https://doi.org/10.3897/zookeys.1044.59475
Figure 2 Rarefaction and extrapolation richness curves for carabid beetles from Armero (A–C), and Armero and Cambao combined (D–F) A, D comparison of richness between habitats using sample-size-based curves B, E sample completeness curves C, F comparison of richness using coverage-based curves. Abbreviations: F = forest, ES = early succession, P = pasture. Numbers in parentheses denote sample sizes and the observed Hill number (q = 0) (A, D), sample size and the estimated sample coverage (B, E), and the estimated sample coverage and the observed Hill number (q = 0) (C, F), respectively.
Figure 2 in Diversity of orb-weaving spiders (Arachnida: Araneae) from tropical dry forest in Northern Colombia, with eleven new records for the country
Figure 2. Distribution of richness and relative abundance (%) by family for each forest.
Figure 2 from: Smith D, Janzen D, Hallwachs W, Smith M (2012) Hyperparasitoid wasps (Hymenoptera, Trigonalidae) reared from dry forest and rain forest caterpillars of Area de Conservación Guanacaste, Costa Rica. Journal of Hymenoptera Research 29: 119-144. https://doi.org/10.3897/jhr.29.3233
Figure 2 - A neighbor-joining tree (NJ) built using Kimura 2 Parameter distance and including 201 sequenced trigonalid specimens from the ACG and North America that have COI sequence greater than 200 bp. Note the divergence between the ACG Taeniogonalos and the North American specimens – and within the dry forest Taeniogonalos fasciatipennisDHJ01 and Taeniogonalos fasciatipennisDHJ02 – all are clearly differentiated by mitochondrial DNA.
Figure 1 from: Smith D, Janzen D, Hallwachs W, Smith M (2012) Hyperparasitoid wasps (Hymenoptera, Trigonalidae) reared from dry forest and rain forest caterpillars of Area de Conservación Guanacaste, Costa Rica. Journal of Hymenoptera Research 29: 119-144. https://doi.org/10.3897/jhr.29.3233
Figure 1 - Color representation of the full length (658 base pairs (bp)) DNA barcodes for each of the 5 ACG trigonalid species. Intra-specific variation in the barcode region is represented by vertical bands in the color bar at that position.
Figures 11-14 from: Smith D, Janzen D, Hallwachs W, Smith M (2012) Hyperparasitoid wasps (Hymenoptera, Trigonalidae) reared from dry forest and rain forest caterpillars of Area de Conservación Guanacaste, Costa Rica. Journal of Hymenoptera Research 29: 119-144. https://doi.org/10.3897/jhr.29.3233
Figures 11-14 - Taeniogonalos fasciatipennis DHJ01. 11 Metasoma, lateral view, female 12 Female armature, sternum 2, ventral view 13 Male paramere, lateral view 14 Male genitalia.
Figures 8-10 from: Smith D, Janzen D, Hallwachs W, Smith M (2012) Hyperparasitoid wasps (Hymenoptera, Trigonalidae) reared from dry forest and rain forest caterpillars of Area de Conservación Guanacaste, Costa Rica. Journal of Hymenoptera Research 29: 119-144. https://doi.org/10.3897/jhr.29.3233
Figures 8-10 - Taeniogonalos fasciatipennis, female. 8 Taeniogonalos fasciatipennisDHJ01, lateral view 9 Taeniogonalos fasciatipennisDHH01, dorsal view 10 Taeniogonalos fasciatipennisDHJ02, lateral view.
Figures 4-7 from: Smith D, Janzen D, Hallwachs W, Smith M (2012) Hyperparasitoid wasps (Hymenoptera, Trigonalidae) reared from dry forest and rain forest caterpillars of Area de Conservación Guanacaste, Costa Rica. Journal of Hymenoptera Research 29: 119-144. https://doi.org/10.3897/jhr.29.3233
Figures 4-7 - Taeniogonalos woodorum. 4 Lateral view, female 5 Dorsal view, female 6 Metasoma, lateral view, female 7 Male genitalia.
Figures 15-20 from: Smith D, Janzen D, Hallwachs W, Smith M (2012) Hyperparasitoid wasps (Hymenoptera, Trigonalidae) reared from dry forest and rain forest caterpillars of Area de Conservación Guanacaste, Costa Rica. Journal of Hymenoptera Research 29: 119-144. https://doi.org/10.3897/jhr.29.3233
Figures 15-20 - Taeniogonalos gundlachii. 15 Lateral view, female 16 Dorsal view, female 17 Metasoma, lateral view, female 18 Female armature, sternum 2, ventral view 19 Male paramere, lateral view 20 Male genitalia.
Figure 6 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 6 - The total individual numbers of the top three dominant species on the burned site from 2008–2015.
Figure 4 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 4 - The frequency of native plants on the unburned site and the burned site per 1 m2. Error bars are ± SD (n=50). T-value = 6.50. P-value < 0.001.
Figure 7 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 7 - The total individual numbers of the top three dominant species on the unburned site from 2008–2015.
Figure 1 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 1 - The species richness on the unburned site and the burned site per 1 m2. Error bars are ± SD (n=50). T-value= 4.70, P-vale < 0.001.
Figure 5 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 5 - The total individual numbers of dominant species on the unburned site and the burned site from 2008–2015.
Figure 3 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 3 - The frequency of lichens, woody plants, forb plants, grass on the unburned site and the burned site per 1 m2. Error bars are ± SD (n=50). Lichens: T-value = 27.71; P-value < 0.001. Woody plants: T-value = 18.96; P-value < 0.001. Forb plants: T-value = -7.90; P-value < 0.001. Grass: T-value = -3.72; P-value =0.001.
Figure 2 from: Lu P-L, DeLay JK (2016) Vegetation and fire in lowland dry forest at Wa'ahila Ridge on O'ahu, Hawai'i. PhytoKeys 68: 51-64. https://doi.org/10.3897/phytokeys.68.7130
Figure 2 - The plant density on the unburned site and the burned site per 1 m2. Error bars are ± SD (n=50). T-value = 6.75. P-value < 0.001.
Data from: Restoration of forest resilience to fire from old trees is possible across a large Colorado dry-forest landscape by 2060, but only under the Paris 1.5 deg. C goal
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Data from: Estimation of aboveground net primary productivity in secondary tropical dry forests using the Carnegie–Ames–Stanford approach (CASA) model
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OpenNeuro
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