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Figure 4 in Effects of dams on demographic structures of amphidromous fish and crustacean species in Caribbean rivers
Figure 4. – Individual number histograms of each species broken down by size classes (mm) (left chart) and cohort extraction (right chart) downstream of the Moreau River in June. Right chart: red curves are each cohort extracted by the model; green curve is the cumulative individuals' number in the modelled age groups. No Macrobrachium heterochirus were caught.
Figure 6 in Effects of dams on demographic structures of amphidromous fish and crustacean species in Caribbean rivers
Figure 6. – Individual number histograms of each species broken down by size classes (mm) for the three stations (top chart) and porosity chart of the Pérou River water intake (bottom chart). Bottom chart: arrow indicates the optimal size at crossing; dotted black line indicates 50% crossing; dotted grey lines indicate the mean crossing rate for these size classes. The size of the downstream and upstream population of Macrobrachium faustinum is too small and fragmented to be presented.
FIGURE 3 in The effects of lithification on fossil assemblage biodiversity and composition: An experimental test
FIGURE 3. Classical (A) and coverage-based (B) rarefaction of the Fort Thompson Formation samples. In each panel, the red curve marks the lithified sample, and the blue curve marks the corresponding unlithified replicate sample. The gray curves mark other unlithified samples taken from different horizons of the same formation at the same outcrop. The red and blue bands mark 95% confidence intervals.
FIGURE 7 in The effects of lithification on fossil assemblage biodiversity and composition: An experimental test
FIGURE 7. Relative abundances of the ten most abundant species in the overall dataset. Relative abundance is plotted on a square-root scale so that low values can be more easily distinguished. A. Bermont Formation. B. Fort Thompson Formation.
FIGURE 6. Principal coordinates analysis. The eigenvalues for the first two axes accounted for 72 in The effects of lithification on fossil assemblage biodiversity and composition: An experimental test
FIGURE 6. Principal coordinates analysis. The eigenvalues for the first two axes accounted for 72% of the variation in the data.
FIGURE 5 in The effects of lithification on fossil assemblage biodiversity and composition: An experimental test
FIGURE 5. Percentage of individuals in each sample belonging to small-shelled species, defined as less than 15 mm. A. Bermont Formation. B. Fort Thompson Formation.
Figure 1. Standard curve for gallic acid y in Effect of extraction solvent system on the antimicrobial, antioxidant and total polyphenol content of the bark of Pistacia chinensis
Figure 1. Standard curve for gallic acid y = absorbance, x = concentration of Gallic Acid, R2 = correlation coefficient.
Fig. 5 in Potential herbicidal effect of synthetic chalcones on the initial growth of sesame, Sesamum indicum L., and brachiaria, Urochloa decumbens (Stapf) R. D. Webster
Fig. 5. Percentage of growth inhibition/stimulus of shoot parts of brachiaria seedlings [Urochloa decumbens (Stapf) R.D. Webster] grown for five days in water solutions containing the chalcones, or analogues, or Glyphosate®, in comparison to the positive control (distilled water). The chalcones are identified in the figure 2. *Indicates a significant difference in relation to the control, p<0.05.
Fig. 4 in Potential herbicidal effect of synthetic chalcones on the initial growth of sesame, Sesamum indicum L., and brachiaria, Urochloa decumbens (Stapf) R. D. Webster
Fig. 4. Percentage of growth inhibition/stimulus of root parts of sesame seedlings (Sesamum indicum L.) grown for five days in water solutions containing the chalcones, or analogues, or Glyphosate®, in comparison to the positive control (distilled water). The chalcones are identified in figure 2. *Indicates a significant difference in relation to the control, p<0.05.
Figs. 1 A, B. A. Richness and B in Influence of the Edge Effect on A Soil Seed BAnk of A NAturAl FrAgment in the AtlAntic Forest
Figs. 1 A, B. A. Richness and B. abundance of the soil seed bank in relation to the edge from Mata Grande of the PEI.
Fig. 3 in Influence of the Edge Effect on A Soil Seed BAnk of A NAturAl FrAgment in the AtlAntic Forest
Fig. 3 NMDS of the composition of the soil seed bank differences in distances from the edge from Mata Grande of the PEI.
Figs. 2 A, B. A in Influence of the Edge Effect on A Soil Seed BAnk of A NAturAl FrAgment in the AtlAntic Forest
Figs. 2 A, B. A Linear regression of the richness and B. abundance of the soil seed bank in relation to the edge from Mata Grande of the PEI (y=Ax+B).
Fig. 3 in Effect of beta 1,3 glucan in stress responses of the pencilfish (Nannostomus trifasciatus) during transport within the rio Negro basin
Fig. 3. Whole-body cortisol levels (mean ± SD) during transportation of pencilfish (Nannostomus trifasciatus) previously fed with different levels of beta 1,3 glucan. No significant differences between all sampling times using the Kruskal-Wallis ANOVA on ranks were observed (P>0.05).0: initial time of transport; 24: 24 hours of transport; 24 AT: 24 hours after transport (recovery time).
Fig. 2 in Effect of beta 1,3 glucan in stress responses of the pencilfish (Nannostomus trifasciatus) during transport within the rio Negro basin
Fig. 2. Net Na+ (A) and K+ (B) fluxes during transportation of pencilfish (Nannostomus trifasciatus) previously fed with different levels of beta 1,3glucan. Positive values indicate net influxes and negative values net effluxes. N = 4 boxes per treatment in each sample time. Different lower case letters indicate significant difference among times of transport within the same group and * indicate significant difference from control group within the same time of transport by Scheirer-Ray-Hare extension of the Kruskal-Wallis test followed by the Nemenyi test (P<0.05).
Fig. 2 in Hydropeaking effects of on the diet of a Neotropical fish community
Fig. 2. Results from multivariate analysis nMDS (nonmetric multidimensional scaling) for fish collected in January and July 2010, downstream from Itutinga Dam, Grande River, in the four flow rate treatments (1 - constant flow rate in January; 2 - hydropeaking in January; 3 - constant flow rate in July; 4 - hydropeaking in July).
Fig. 1 in Hydropeaking effects of on the diet of a Neotropical fish community
Fig. 1. Schematic drawing of the Grande River basin upstream from Furnas Reservoir. The study area is highlighted by a black circle.
Fig. 4 in Hydropeaking effects of on the diet of a Neotropical fish community
Fig. 4. Relationship among the diet dissimilarity between seasons and diet dissimilarity stable and hydropeaking treatments in January (a) and July (b). Line is representing a linear correlation. Correlation values (r and p) are indicated. Aa= Apareiodon affinis; Aal= Astyanax altiparanae; Af= Astyanax fasciatus; Bs= Bryconamericus stramineus; Cn= Cyphocharax nagelii; Ev= Eigenmmania virescens; Hy1= Hypostomus sp.1; Hym= Hypostomus aff. margaritifer; Ihe= Iheringichthys labrosus; Km= Knodus moenkhausii; La= Leporinus amblyrhynchus; Lo= Leporinus octofasciatus; Pa= Piabina argentea; Pm= Pimelodus maculatus; Sn= Schizodon nasutus.
Fig. 3 in Hydropeaking effects of on the diet of a Neotropical fish community
Fig. 3. Average frequency of occurrence of food items in the analyzed treatments based on SIMPER analysis, downstream from Itutinga Dam, Grande River. a - Assemblage level; b - Invertivores guild; c - Iliophagous guild; d - Generalists guild; e - Herbivores guild.
Fig. 1 in Effect of water temperature and prey concentrations on initial development of Lophiosilurus alexandri Steindachner, 1876 (Siluriformes: Pseudopimelodidae), a freshwater fish
Fig. 1. Total length of Lophiosilurus alexandri after 15 days of exogenous feeding. The graph "A" and "B" showed the best temperature for the prey concentration P 700 and P 1,300, respectively.
Fig. 2 in Effect of water temperature and prey concentrations on initial development of Lophiosilurus alexandri Steindachner, 1876 (Siluriformes: Pseudopimelodidae), a freshwater fish
Fig. 2. Mean body weight of Lophiosilurus alexandri after 15 days of exogenous feeding. Different letters represent significant differences (P<0.05) among temperatures (a, b, c and d) and prey concentrations (x and y).
ScienceDex guides
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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.