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3,136 results for “Terrestrialization”
Fig. 3 in Formation Dynamics Of Herpetocomplexes On Sections Of Secondary Succession In Terrestrial Ecosystems Of Belarus
Fig. 3. Changes in species diversity (D, Simpson index of diversity) of herpetocomplexes at sites of secondary succession.
Fig. 1 in Formation Dynamics Of Herpetocomplexes On Sections Of Secondary Succession In Terrestrial Ecosystems Of Belarus
Fig. 1. Formation the species composition of amphibians and reptiles faunal complexes on sections restoration succession (deforestation site).
Figure 4 in Dactylorhiza Fuchsii (Druce) Soó As A Model Object In In Vitro Culture Study For Development Of Terrestrial Orchids
Figure 4. Root of D. fuchsii growing in the Figure 5. Root of D. fuchsii one year after exposition in NBG: arrow indicates elaborate transplanting ex vitro: arrow indicates some coiled structures known as pelotons of peloton-like structure as they do within the orchid mycorrhizal fungi in the root cortex (section was cells (section was stained with Trypan Blue; bar stained with Trypan Blue; bar = 50 mm) = 50 mm).
Figure 1 in Dactylorhiza Fuchsii (Druce) Soó As A Model Object In In Vitro Culture Study For Development Of Terrestrial Orchids
Figure 1. Development of Dactylorhiza fuchsii (Druce) Soó in vitro conditions: A – beginning of morphogenesis after germination with development of protocorms, characteristic for orchids; B – initialization of rooting; C – sterile plantlets after exposition at 2 °C in the dark, simulating the natural dormancy period; D – plantlet before transplanting ex vitro (ro – root; tu – tuber).
FIGURE 2 in Exotic Terrestrial Macro-Invertebrate Invaders in California from 1700 to 2015: An Analysis of Records
FIGURE 2. Total number of invertebrates detected in Cal- FIGURE 3. Plot of CUSUM values for counts of exotic ifornia 1935–2010. arthropods recorded in California over the period 1935 to 2010.
Figure 3 in Effects of combined treatment of cadmium and oxytetracycline on the terrestrial isopod Porcellio leavis
Figure 3. Concentration of biochemical parameters: Total protein, Lipid peroxidation (LPO), Catalase activity (CAT) and Total free amino acids (TFAA) in P. leavis in different treated groups control, Cd, T1, T2, and T3. Values are the mean of three replicates (n=3) ± SE. The significant difference between the groups were analysed by one-way analysis of variance. Mean values of different subscript letters (a,b,c,d) were significantly different (p<0.001).
FIGURE 1 in Exotic Terrestrial Macro-Invertebrate Invaders in California from 1700 to 2015: An Analysis of Records
FIGURE 1 (left). Examples of non-native macro-terrestrial arthropods that have been detected in California. A. Avocado thrips, Scirtothrips perseae Nakahara (Thysanoptera: Thripidae). (Detected 1992). B. Brown widow spider, Latrodectus geometricus Koch (Araneae: Theridiidae) (detected 2003). C. Glassy-winged sharpshooter, Homalodisca vitripennis (Germar) (Hemiptera: Cicadellidae) (detected 1994). D. Brown marmorated stink bug, Halyomorpha halys Stål (Hemiptera: Pentatomidae) (detected 2005). E. Citrus leafminer, Phyllocnistis citrella Stainton (Lepidoptera: Gracillariidae) (detected 1999). F. Asian citrus psyllid, Diaphorina citri Kuwayama (Hemiptera: Psyllidae) (detected 2008). G. Palm weevil, Rhynchophorus vulneratus (Panzer) (Coleoptera: Curculionidae) (detected 2010) (eradicated 2015). H. Gold spotted oak borer, Agrilus auroguttatus Waterhouse (Coleoptera: Buprestidae) (detected 2004).
Fig. 6 in Exploring the evolution and terrestrialization of scorpions (Arachnida: Scorpiones) with rocks and clocks
Fig. 6 Time tree _or scorpions in_erred in MCMCTree under the correlated rate model (Yang 2007), using 9 so_t upper and hard lower bounded calibrations derived _rom the scorpion _ossil record (see Tables 2 and 3). Node bars = 95% HPD intervals. Gold circles represent _ossil node-calibration minima
Fig. 5 in Exploring the evolution and terrestrialization of scorpions (Arachnida: Scorpiones) with rocks and clocks
Fig. 5 Scorpion calibration _ossils, as speci_ied in Table 1. a Dolichophonus loudonensis, scale 1 cm. b Compsoscorpius buthiformis, scale 1 cm. c Electrochaerilus buckleyi, scale 1 mm. d Protoischnurus axelrodurum, scale 1 cm. e Uintascorpio halandrasi, scale 1 cm. Images a and b belong to the authors. Image c reproduced with permission _rom SantiagoBlay et al. (2004a). Image e reproduced with permission _rom Santiago-Blay et al. (2004b). Image d courtesy o_ Wilson Lourenço
Fig. 4 in Exploring the evolution and terrestrialization of scorpions (Arachnida: Scorpiones) with rocks and clocks
Fig. 4 Maximum likelihood tree in_erred in IQ-TREE under LG+F+I+G4 model (Le and Gascuel 2008). Nodal support values determined _rom 1000 ultra_ast bootstrap replicates (Minh et al. 2013; Hoang et al. 2018). Scale bar = branch length
Fig. 1 in Exploring the evolution and terrestrialization of scorpions (Arachnida: Scorpiones) with rocks and clocks
Fig. 1 General consensus of internal phylogenetic relationships of Chelicerata at present. Question marks represent uncertainty surrounding the monophyly of mites and ticks (Acari) and the unresolved marine life habit of early scorpions
Figure 3 in Harbor seal use of glacier ice and terrestrial haul-outs in the Kenai Fjords, Alaska
Figure 3. Population trends of harbor seals on the southeastern Kenai Peninsula during pupping (Panel A) and the molt (Panel B) based on aerial surveys conducted from 2004 to 2013.
Figure 6 in Harbor seal use of glacier ice and terrestrial haul-outs in the Kenai Fjords, Alaska
Figure 6. Proportion of harbor seal pups counted during pupping relative to total seals (including pups) during pupping (Panel A) and during the subsequent molt (Panel B) at glacial ice (blue) and terrestrial (brown) haul-outs among different locations and time periods. The box (bounded by 13%–23%) represents range of the percent of pups to total seals counted at terrestrial haul-outs outside of Alaska (Venables and Venables 1955, Boulva 1975, Boulva and McLaren 1979, Brown and Mate 1983, Calambokidis et al. 1987). The vertical bar within the box represents the proportion of pups born into an increasing population in British Columbia (Bigg 1969). * designates proportions derived from mean values adjusted for standardized environmental conditions. Sources include (Hoover 1983; Calambokidis et al. 1987; Pitcher 1990; Mathews 1995; Jemison et al. 2006, 2016; Mathews and Pendleton 2006; Womble et al. 2010; Mathews et al. 2016; Kenai Fjords National Park, unpublished).
Figure 5 in Harbor seal use of glacier ice and terrestrial haul-outs in the Kenai Fjords, Alaska
Figure 5. Comparison of numbers of mother-pup harbor seal pairs (MP) counted in Aialik Bay and Northwestern Fjord from 2004 to 2013 using multiple survey methods. Area charts indicate maximum annual counts of MP in Aialik Bay and Northwestern Fjord (light blue) and in Aialik Bay (darker blue). Maximum annual MP counts in Northwestern Fjord are indicated by the blue green line. White dots with 95% CI error bars show generalized linear model (GLM) mean estimate MP based on remote video observations in Aialik Bay during standardized favorable haul-out conditions.
Figure 4 in Harbor seal use of glacier ice and terrestrial haul-outs in the Kenai Fjords, Alaska
Figure 4. Comparison of regional changes in numbers of harbor seal pups (Panel A), seals without pups present during pupping (Panel C), and molting seals (Panel D) in four regions of the coastline extending from McCarty Fjord through Johnstone Bay. Pup counts at individual fjords summarized as RB-JB are compared in Panel B. Bars represent maximum counts obtained during aerial surveys. Total counts for all regions (black dots) are measured on the secondary axis. Histogram bars of molt counts represent maximum counts for each year obtained from aerial surveys; triangles indicate counts in Northwestern Fjord based on KFT vessel surveys.
Figure 1 in Harbor seal use of glacier ice and terrestrial haul-outs in the Kenai Fjords, Alaska
Figure 1. Maps showing locations of the study area (Panel A) and of study area place names (Panel B). Red shading along the coastline, in the Panel A inset, illustrates the geographic extent of surveys (portions of flights flown at altitudes <335 m).
Fig. 20 in Forbidden islands. The absence of endemics among the insular non-volant terrestrial mammalian fauna of the Red Sea
Fig. 20 - Fragment of decoration on a memorial temple to the Egyptian queen Hatshepsut (15th century BC) of the 18th Dynasty (Deir el-Bahari, Upper Egypt). It shows a baboon climbing a doum palm, Hyphaene thebaica (L.) Mart., 1838; a herd of long-horn cattle; and the head of a sub-adult giraffe, Giraffa camelopardalis L., 1758, from the mythical Land of Punt.
Fig. 7 in Forbidden islands. The absence of endemics among the insular non-volant terrestrial mammalian fauna of the Red Sea
Fig. 7 - Skull of a subadult female of �rabian hamadryas baboon, Papio hamadryas arabicus Thomas, 1900, found on the island of Farasan Kebir in �pril 1984 (photo by Saulo Bambi; courtesy of the Museo di Storia Naturale dell'Universita di Firenze, Sezione di Zoologia "La Specola").
Fig. 17 in Forbidden islands. The absence of endemics among the insular non-volant terrestrial mammalian fauna of the Red Sea
Fig. 17 - Skull of an adult female of the extant Farasan gazelle, Gazella gazella farasani Thouless & �l Bassri, 1991 (catalogue number: MZUF 11330, Zoological Museum, University of Florence) (photo Saulo Bambi; courtesy of the Museo di Storia Naturale dell'Universita di Firenze, Sezione di Zoologia "La Specola", Florence).
Fig. 21 in Forbidden islands. The absence of endemics among the insular non-volant terrestrial mammalian fauna of the Red Sea
Fig. 21 - Skull of an adult male domestic goat collected on the island of Dumsuq (Farasan archipelago, Saudi �rabia) in 1984. It is evidence of the deliberate introduction of mammals by man to the Red Sea islands. It is another specimen of the Somali ethnic group, but in this case a primitive type, with straight, involute horns (photo by Saulo Bambi, courtesy of the Museo di Storia Naturale dell'Universita di Firenze, Sezione di Zoologia "La Specola").
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.