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1,659 results for “Population: structure”
Fig. 6 in Phenology And Population Structure Of Forest Herbaceous Species In Artificial And Natural Communities In The Steppe Zone Of Ukraine
Fig. 6. The age structure of populations in natural plant community: a – association of Corydalis solida (1) + Anemonoides ranunculoides (2) + Ficaria verna (3) + Corydalis marschalliana (4); b –Association Ficaria verna (5) + Corydalis solida (6) + Viola odorata + Fragaria vesca.
Fig. 7 in Phenology And Population Structure Of Forest Herbaceous Species In Artificial And Natural Communities In The Steppe Zone Of Ukraine
Fig. 7. The age structure of populations of spring ephemeroids under artificial plant community conditions (1) and natural ravine forest (2): a – Corydalis solida, b – Ficaria verna, c – Anemonoides ranunculoides.
Fig. 1 in Phenology And Population Structure Of Forest Herbaceous Species In Artificial And Natural Communities In The Steppe Zone Of Ukraine
Fig. 1. The age structure of populations in artificial plant community: a – association of Ficaria verna (1) + Anemonoides blanda (2) + Corydalis solida (3), b – "Ficaria verna (3)" to "Ficaria verna (4)"; "Anemonoides blanda (4)" - "Anemonoides blanda (5)"; "Corydalis solida (5)" – "Corydalis solida (6)".
Fig. 10 in Phenology And Population Structure Of Forest Herbaceous Species In Artificial And Natural Communities In The Steppe Zone Of Ukraine
Fig. 10. Influence of January-April total precipitation value on the date of Primula veris budding onset.
Fig. 2 in Phenology And Population Structure Of Forest Herbaceous Species In Artificial And Natural Communities In The Steppe Zone Of Ukraine
Fig. 2. The age structure of populations in artificial plant community: a - association Anemonoides ranunculoides (1) + Corydalis solida (2) + Corydalis marschalliana, b - association Ficaria verna (3) + Anemonoides ranunculoides (4) + Anemonoides nemorosa, (5) + Corydalis solida (6).
Figure 5 in Landscape biogeography and population structuring of a facultatively amphidromous galaxiid fish, Galaxias brevipinnis
Figure 5. – Bar plots showing density of Galaxias brevipinnis larvae per m3 of water in plume, near shore, and off shore sites in large river (left) and small river (right) sites. The Dart River, Reese River, Greenstone River, and Buckler Burn are tributaries of Lake Wakatipu while Makarora River, Matukituki River, Boundary Creek, and Albert Burn are tributaries of Lake Wānaka. No larvae were collected in near shore and off shore samples from Greenstone River.
Figure 3. – Average STRUCTURE results aggregated using CLUMPAK for populations 2–6 and 9. K in Landscape biogeography and population structuring of a facultatively amphidromous galaxiid fish, Galaxias brevipinnis
Figure 3. – Average STRUCTURE results aggregated using CLUMPAK for populations 2–6 and 9. K = 6 was selected as the most likely population estimate using Evanno's method. STRUCTURE initially separated the lakes draining to the east coast (L. Wānaka and L. Wakatipu) from all other sites at K = 2. The West Coast lakes were split away next (K = 3), with L. Moeraki and L. Paringa splitting at K = 4 and L. Cristabel at K = 5. East coast L. Wānaka and L. Wakatipu were split at K = 6. L. Paringa and L. Moeraki are split form each other at K = 9.
FIGURE 5 in Dancing with the devil: courtship behaviour, mating evidences and population structure of the Mobula tarapacana (Myliobatiformes: Mobulidae) in a remote archipelago in the Equatorial Mid-Atlantic Ocean
FIGURE 5 | Distinct courtship behaviors of sicklefin devil rays Mobula tarapacana observed in the Saint Peter and Saint Paul Archipelago. A. Female being chased by two males. B. Male overlapping female. C. Male trying to overlap on female. D. Male overlaps the female with two more males chasing. E–F. Sequence of male following female.
FIGURE 3 in Dancing with the devil: courtship behaviour, mating evidences and population structure of the Mobula tarapacana (Myliobatiformes: Mobulidae) in a remote archipelago in the Equatorial Mid-Atlantic Ocean
FIGURE 3 | Female (grey) and male (black) Mobula tarapacana size distribution (disk width- DW, in meters) per month, in the Saint Peter and Saint Paul Archipelago (SPSPA), from December 2008 to June 2016. Red dashed line= size at maturity for males (White et al., 2006); blue dashed line= size at maturity for females (Notarbartolo di Sciara, 1988).
Figure 3 in Infraspecific genetic variation and population structure of Salvia nemorosa L. (Lamiaceae) in Iran
Figure 3. PCoA plot of the studied populations based on ISSR data (population numbers are according to Table 1).
Figure 2 in Infraspecific genetic variation and population structure of Salvia nemorosa L. (Lamiaceae) in Iran
Figure 2. MDS plot of the studied populations based on ISSR data (population numbers are according to Table 1).
Figure 4 in Infraspecific genetic variation and population structure of Salvia nemorosa L. (Lamiaceae) in Iran
Figure 4. NJ tree of S. nemorosa populations based on ISSR results (population numbers are according to Table 1).
Figure 2 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 2. Insects associated with Encephalartos eugene-maraisii in Entabeni: A, B, Amorphocerus cf. setosus; C, D, Apinotropis verdoornae; E, F, Zerenopsis lepida. Photographs: P.D. Janse van Rensburg.
Figure 4 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 4. Large Encephalartos eugene-maraisii stem that was pushed over by poachers. Photographer: P.D. Janse van Rensburg.
Figure 1 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 1. Typical architecture of an Encephalartos eugene-maraisii plant. Photographer: P.D. Janse van Rensburg.
Figure 3 in Impact of poaching on the population structure and insect associates of the Endangered Encephalartos eugene-maraisii from South Africa
Figure 3. Distribution of Encephalartos eugene-maraisii in the Entabeni Safari Conservancy between 2021 and 2022, compared to 2008. A, heatmap of E. eugene-maraisii plants re-recorded between 2021 and 2022; B, heatmap of E. eugene-maraisii plants that were not relocated. Lines indicate the fence line. The map is given without a geographical reference because E. eugene-maraisii is vulnerable to poaching.
Figure 1 in The population structure of Mesobuthus gibbosus (Scorpiones: Buthidae) on Koufonisi Island (central Aegean Archipelago, Greece)
Figure 1: The geographic position of Koufonisi (red dot) in Greece and the location of the study site at Pori bay (in red).
Figure 8 in Genetic variability and population structure of some Iranian Salvia limbata C. A. Mey. populations
Figure 8. TCS network of the studied S. limbata and their individuals (numbers indicated the populations based on Table 1).
Figure 6 in Genetic variability and population structure of some Iranian Salvia limbata C. A. Mey. populations
Figure 6. STRUCTURE analysis of the studied populations, which revealed the best number of K=7 (numbers indicated the populations based on Table 1).
Figure 5 in Genetic variability and population structure of some Iranian Salvia limbata C. A. Mey. populations
Figure 5. NJ tree of the evaluated populations and their individuals based on ISSR data (numbers indicated the populations based on Table 1).
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Allen Brain Atlas
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International Brain Laboratory public data
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OpenNeuro
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