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FIG. 3 in Le site paléontologique du Grand Morier (Pont-Boutard, Indre-et-Loire, France): contexte géologique et détail biostratigraphique des formations cénozoïques à partir des assemblages de vertébrés fossiles
FIG. 3. — Coupe géologique de direction ouest-est extraite de la carte géologique de Pont-Boutard (Fig. 2) passant par le site paléontologique du Grand Morier. L'échelle des altitudes est exagérée volontairement pour améliorer la lisibilité du graben de Pont-Boutard.
FIG. 1 in Le site paléontologique du Grand Morier (Pont-Boutard, Indre-et-Loire, France): contexte géologique et détail biostratigraphique des formations cénozoïques à partir des assemblages de vertébrés fossiles
FIG. 1. — Vue générale de la falunière du Grand Morier (Pont-Boutard, Indre-et-Loire, France) en exploitation en 1994.
FIG. 5 in Le site paléontologique du Grand Morier (Pont-Boutard, Indre-et-Loire, France): contexte géologique et détail biostratigraphique des formations cénozoïques à partir des assemblages de vertébrés fossiles
FIG. 5. — Colonnes lithostratigraphiques (Log 1, Log 2 et Log 3) levées sur le site paléontologique du Grand Morier pendant l'exploitation de la falunière. Leurs localisations exactes sont spécifiées sur la carte géologique de Pont- Boutard (Fig. 2): 1, argile sableuse verte (Éocène); 2, calcaire lacustre avec ses poches d'argile noire de décalcification à son sommet (Oligocène-Agénien supérieur); 3, sable continental (Orléanien inférieur); 4, calcarénite à strates oblique (Burdigalien supérieur-Langhien inférieur); 5, conglomérat de la base des faluns à bryozoaires (Langhien-Tortonien inférieur); 6, falun à bryozoaires (Tortonien); 7, limons des plateaux chapeautés par la terre végétale actuelle (Quaternaire-Actuel).
FIG. 7 in Le site paléontologique du Grand Morier (Pont-Boutard, Indre-et-Loire, France): contexte géologique et détail biostratigraphique des formations cénozoïques à partir des assemblages de vertébrés fossiles
FIG. 7. — Exemples de fossiles de mammifères cénozoïques du Grand Morier (Pont-Boutard, Indre-et-Loire, France) provenant de la collection Quétin du Musée du Savignéen (Savigné-sur-Lathan, Indre-et-Loire, France): A, Paratapirus intermedius (Filhol, 1885) (assemblage n°2), hémimandibule d. portant m1-2 (2012-PBT-4); B, Prodeinotherium bavaricum Von Meyer, 1831 (assemblage n°6), M2 d. isolée (2012-PBT-289); C, D, Diaceratherium aurelianense (Nouel, 1866) (assemblage n°5); C, M3 g. isolée (2012-PBT-51); D, M3 d. isolée (2012-PBT-49); E-K, Protaceratherium minutum (Cuvier, 1822-1824) (assemblages n°2 et n°5); E, P3 d. isolée (2012-PBT-137); F, P4 g. isolée (2012-PBT-139); G, P3 g. isolée (2012-PBT-136); H, montage d'une série dentaire portant P1-3 g. (2012-PBT-135); I, M1 g. isolée (2012-PBT-128); J, M2 d. isolée (2012-PBT-130); K, Plagiolophus cf. annectens (Owen, 1847) (assemblage n°1), p4 ou m1 g. isolée (LB-PBT-1). Échelles: 1 cm.
Figure 3 in Corals and reefs of Cosmoledo and Aldabra atolls: Extent of damage, assemblage shifts and recovery following the severe mortality of 1998
Figure 3. Visual estimates of coral cover at various depths on seaward slopes (diamonds) and lagoon patch reefs (open circles). The dotted curve indicates hypothetical or possible approximate maximum pre-bleaching coral cover with depth, based on maximum values found in patches here at shallow and intermediate depths. The solid curve is a third-order polynomial fit of the seaward reef cover values. Average seaward reef mortality is suggested by the gap between the two curves. The arrow marks the approximate transition depth.
Figure 2 in Corals and reefs of Cosmoledo and Aldabra atolls: Extent of damage, assemblage shifts and recovery following the severe mortality of 1998
Figure 2. (a) Seaward reef slope of West Cosmoledo. This is typical of shallow seaward slopes of south, through west to the north, showing very limited coral growth, but presence of algae. (b) Dead Millepora colonies in the lagoon are extensive, without sign of live growth and few new recruits. (c) Acropora palifera, showing recovery on shallow seaward slopes. It is growing on the side of a large dead colony of the same species. (d) Dead Acropora cytherea, eroded but still standing. Most examples in November 2002 were remnants of stumps. A new Acropora has since settled on the table. The yellow device is a newly installed temperature logger.
Figure 1 in Corals and reefs of Cosmoledo and Aldabra atolls: Extent of damage, assemblage shifts and recovery following the severe mortality of 1998
Figure 1. The Aldabra group of atolls, showing survey sites. Top left: location map, rectangle shows location of the four components of the Aldabra group; top right: World Vector Shoreline outline of the four groups; lower right: Cosmoledo Atoll (scanned image from map); lower left: Aldabra (from a Landsat MSS). On lower maps, dots indicate sample sites in lagoon and seaward sites, rectangles indicate sample sites in main channels. In Cosmoledo, lagoon sites are pooled. On seaward side of Cosmoledo, sites were West (Menai Island), North (North Island) and North-West (midway between the two). Seaward site in Aldabra was 300–500 m north of the field station (marked by ×). All sites in Cosmoledo lagoon had radii of at least 100 m, or, on seaward sites, along at least 200 m of reef between 0 and 30 m depth.
Figure 3 in Factors influencing spatial and temporal structure of frog assemblages at ponds in southeastern Brazil
Figure 3. Distribution of nine tadpole species within ponds at Santuário do Caraça, southeastern Brazil, according to variables used to describe microhabitats used by them and period of occurrence, in the first three axes of discriminant space. In the first discriminant axis, smaller values represent larger association to the bottom. In the second axis, the largest values indicate use of deeper microhabitats by tadpoles. In the third axis, larger values indicate species that used both microhabitats with and without aquatic vegetation, and lower values indicate species that used only microhabitats with aquatic vegetation. Centroids for each species are shown on the right.
Figure 1 in Factors influencing spatial and temporal structure of frog assemblages at ponds in southeastern Brazil
Figure 1. Mean monthly temperatures and monthly rainfall at the study site between September 2003 and December 2004.
Figure 2 in Factors influencing spatial and temporal structure of frog assemblages at ponds in southeastern Brazil
Figure 2. Distribution of adult individuals of 22 anuran species at Santuário do Caraça, southeastern Brazil, according to variables used to describe microhabitat use and activity periods, in the first three axes of the discriminant function. Centroids for each species are shown on the right.
Fig. 4 in Influence Of Environmental Cycles Upon A Seagrass Caridean Shrimp Assemblage
Fig. 4. Two-dimensional nMDS scaling configuration. Plotted on the figure are 70% Bray-Curtis similarity clusters calculated using PRIMER
Fig. 2 in Influence Of Environmental Cycles Upon A Seagrass Caridean Shrimp Assemblage
Fig. 2. Mean (+S.E.) shrimp assemblage characteristics at the different sampling times during the lunar, tidal and diel cycle.
Fig. 4 in A comparison of ground-dwelling and arboreal ant assemblages (Hymenoptera: Formicidae) in lowland forests of Cambodia
Fig. 4. Non-metric multidimensional scaling ordination for grounddwelling ants in community forest (Kampong Chhnang), regrowth and natural forests (Kampong Thom). Circle: ground samples in community forest; triangle: ground samples in regrowth forest; square: ground samples in natural forest.
Fig. 2 in A comparison of ground-dwelling and arboreal ant assemblages (Hymenoptera: Formicidae) in lowland forests of Cambodia
Fig. 2. Surveyed lowland forests of Cambodia. A, community forest in Kampong Chhnang Province; B, regrowth forest in Kampong Thom Province; C, natural forest in Kampong Thom Province.
Fig. 5 in A comparison of ground-dwelling and arboreal ant assemblages (Hymenoptera: Formicidae) in lowland forests of Cambodia
Fig. 5. Non-metric multidimensional scaling ordination for arboreal ants in community forest (Kampong Chhnang), regrowth and natural forests (Kampong Thom). Circle: arboreal samples in community forest; triangle: arboreal samples in regrowth forest; square: arboreal samples in natural forest.
Fig. 3. A in A comparison of ground-dwelling and arboreal ant assemblages (Hymenoptera: Formicidae) in lowland forests of Cambodia
Fig. 3. A, Mean species richness (with S.D.) of ants per transect in community, regrowth and natural forests; B, Species richness in community, regrowth and natural forests of Cambodia. The dark band indicates the number of overlapping species between ground and arboreal samples.
Fig. 1 in A comparison of ground-dwelling and arboreal ant assemblages (Hymenoptera: Formicidae) in lowland forests of Cambodia
Fig. 1. Map of study sites in Kampong Chhnang and Kampong Thom Provinces, Cambodia. CF, community forest in Kampong Chhnang Province; RF, regrowth forest; NF, natural forest in Kampong Thom Province.
Fig. 6 in Do habitat, month and environmental parameters affect shrimp assemblage in a shallow semi-enclosed tropical bay, Thailand?
Fig. 6. Biplots of some shrimp species and environmental variables (arrows) on the first two canonical axes derived from CCA of shrimp abundance and environmental variables in Pattani bay during February 2011 and January 2012.
Fig. 3 in Do habitat, month and environmental parameters affect shrimp assemblage in a shallow semi-enclosed tropical bay, Thailand?
Fig. 3. Relative density (%) and species richness of shrimps collected in different months in Pattani Bay between February 2011–January 2012 at five different habitats.
Fig. 4 in Do habitat, month and environmental parameters affect shrimp assemblage in a shallow semi-enclosed tropical bay, Thailand?
Fig. 4. Cluster dendogram demonstrating grouping of shrimps by month and habitat (Jan…Dec = January…December; Sa = sandy habitat, Ma = Mangrove habitat, S = Shell-deposited habitat, Mu = Muddy habitat and G = Seagrass habitat; G1, 2, 3 = cluster group 1, 2, and 3).
ScienceDex guides
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These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
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.