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Fig. 5 in Experimental Chronic Exposure rotunda to Zinc of the Foraminifer Pseudotriloculina
Fig. 5. Biomass variations at each experimental time for each zinc concentration (T x –T 0). At C5 = 100 mg/L biomass variation was zero. Time (T) is expressed as weeks from the start of the experiment.
Fig. 7 in Experimental Chronic Exposure rotunda to Zinc of the Foraminifer Pseudotriloculina
Fig. 7. Total biomass variation (T 10–T0) at each zinc concentration. Results of regression analysis are shown (P-value <0.05).
Figure 4 in Induction of histopathological lesions in renal tissue of the fish Labeo rohita upon exposure to municipal wastewater of Tung Dhab Drain, Amritsar, India
Figure 4. Light micrographs of histological sections of kidney taken from fish L. rohita exposed to municipal wastewater concentrations for exposure durations of 15 (A; 35.4%), 30 (B; 17.7%, C; 26.6%), 60 (D; 26.6%, E; 35.4%) days, and recovery experiments of 60 days (F; 35.4%). The histopathological alterations were marked by () occlusion of tubular lumen; () hyaline droplet degeneration; () dilation of glomerular capillaries; () reduction of Bowman's space; () melanomacrophage centers; () nuclear hypertrophy; () cellular hypertrophy; () cytoplasmic vacuolation in the interrenal cells; () necrosis. Magnification 100×.
Figure 3 in Induction of histopathological lesions in renal tissue of the fish Labeo rohita upon exposure to municipal wastewater of Tung Dhab Drain, Amritsar, India
Figure 3. Kidney mean DTC values in fish L. rohita exposed to municipal wastewater for durations of 15 days (a), 30 days (b), 60 days (c) when compared to control, and (d) subjected to recovery experiments for 60 days and compared with treated group. Values are mean ± SE (vertical bars); means followed by different letters are significantly different from each other (Tukey's post-hoc test, P ≤ 0.01).
Figure 2 in Induction of histopathological lesions in renal tissue of the fish Labeo rohita upon exposure to municipal wastewater of Tung Dhab Drain, Amritsar, India
Figure 2. Histological sections of kidney of fish L. rohita taken as control. A. Posterior kidney showing renal corpuscle formed by Bowman's capsule (BC), Bowman's space (BS), and Glomerulus (G). PT: proximal tubule; distal tubule. B. Anterior kidney showing chromaffin cells (CC) and interrenal cells (IC). Magnification 100×.
Figure 1 in Induction of histopathological lesions in renal tissue of the fish Labeo rohita upon exposure to municipal wastewater of Tung Dhab Drain, Amritsar, India
Figure 1. Map showing Tung Dhab Drain and Hudiara Drain. (a) The sampling site is marked by a star (); origin of drains is shown by (); confluence of Tung Dhab Drain and Hudiara Drain is marked by (). (b) Map showing main industries and sewer outfalls along Tung Dhab Drain. () indicates sewer outfalls; () metal foundries; () paper mill; () food; () leather; () chemical industries. Source: Adapted from Google Earth Maps, accessed August 2014.
Figure 4 in Study of histoarchitectural changes in Anopheles stephensi larvae following exposure to Eucalyptus globulus and Aloe vera oils
Figure 4. Longitudinal section of thorax highlighting the gastric ceca of 4th instar Anopheles stephensi larvae (40×): (a) Control larva having epithelial cells (EC), vesicles (V), nucleus (N), peritrophic membrane (PM), basement-membrane (BM), muscle fibers (MF), microvilli (MV); (b) Eucalyptus globulus oil treated larva showing diversifications in various regions; (c) Aloe vera oil treated larva showing rifts in peritrophic membrane (PM).
Figure 3 in Study of histoarchitectural changes in Anopheles stephensi larvae following exposure to Eucalyptus globulus and Aloe vera oils
Figure 3. Longitudinal sections of head highlighting the region of imaginal bud of antennae (IBA) of 4th instar Anopheles stephensi larvae (40×): (a) Control larva showing intact IBA; (b) Eucalyptus globulus oil treated larva showing cracks and disorganization in IBA; (c) Aloe vera oil treated larva showing stretching and elongation in IBA.
Figure 5 in Study of histoarchitectural changes in Anopheles stephensi larvae following exposure to Eucalyptus globulus and Aloe vera oils
Figure 5. Longitudinal sections of abdomen of 4th instar Anopheles stephensi larvae (10×): (a) Control larva showing lumen (L) and muscle fibers (MF); (b) Eucalyptus globulus oil treated larva showing disintegration; (c) Aloe vera oil treated larva showing perturbation and lesions in the alimentary canal.
Figure 7 in Study of histoarchitectural changes in Anopheles stephensi larvae following exposure to Eucalyptus globulus and Aloe vera oils
Figure 7. Longitudinal sections of midgut region highlighting fat bodies of 4th instar Anopheles stephensi larvae (40×): (a) Control larva showing deposition of fat bodies (FB); (b) Eucalyptus globulus oil treated larva showing disappearance of fat bodies (FB) in various areas; (c) Aloe vera oil treated larva showing very little disruption of fat bodies (FB).
Figure 1Sampling site and stations.1A in Living in the sunlight: micro-environments with higher exposure of sunlight have more abundance and diversity of Hymenoptera in a Brazilian Atlantic Forest fragment
Figure 1Sampling site and stations.1A) Study area including the RAPELD modules.Each black point represents a permanent plot.1B) Trap-nest stations and selected micro-environments: treefall gap (A), placed in wooden post at 1.5m height; understory (B), placed in a tree branch at approximately 1.5 meters height; canopy (C), suspended with thread in a tree (height between 19.0 and 9.1 meters).
Figure 2 in Living in the sunlight: micro-environments with higher exposure of sunlight have more abundance and diversity of Hymenoptera in a Brazilian Atlantic Forest fragment
Figure 2 Interpolation curves of the richness and diversity of trap-nesting Hymenoptera (Atlantic forest, Brazil) in relation to the lowest observed abundance brood cells sampled and assessed for three Hill numbers (0, 1 e 2). CAN= canopy; GAP= treefall gap; UND= Understory.
Figure 1 in Compatibility of entomopathogenic nematodes with plant extracts and post-exposure virulence test under laboratory condition
Figure 1. Percentage survival of the EPN Species in aqueous and ethanol extracts of A. amatymbica and E. elephantina after 72 h exposure. Different lower-case characters represent significant differences at p <0.05.
Figure 6 in Effects of in vivo exposures to nanoparticles (Al O , CuO, TiO ) on the activities of ATPases in the gill and muscle of freshwater mussel (Unio tigridis)
Figure 6. Effects of NPs on Ca-ATPase activity in the muscle of mussels after 14 days. * indicates significant (p <0.05) differences compared to control.
Figure 4 in Effects of in vivo exposures to nanoparticles (Al O , CuO, TiO ) on the activities of ATPases in the gill and muscle of freshwater mussel (Unio tigridis)
Figure 4. Effects of NPs on Ca-ATPase activity in the gill of mussels after 14 days. * indicates significant (p <0.05) differences compared to control.
Figure 3 in Effects of in vivo exposures to nanoparticles (Al O , CuO, TiO ) on the activities of ATPases in the gill and muscle of freshwater mussel (Unio tigridis)
Figure 3. Effects of NPs on Mg-ATPase activity in the gill of mussels after 14 days. * indicates significant (p <0.05) differences compared to control.
Figure 5 in Effects of in vivo exposures to nanoparticles (Al O , CuO, TiO ) on the activities of ATPases in the gill and muscle of freshwater mussel (Unio tigridis)
Figure 5. Effects of NPs on Mg-ATPase activity in the muscle of mussels after 14 days. * indicates significant (p <0.05) differences compared to control.
Figure 1 in Effects of in vivo exposures to nanoparticles (Al O , CuO, TiO ) on the activities of ATPases in the gill and muscle of freshwater mussel (Unio tigridis)
Figure 1. TEM images of Al O (a), CuO (b), and TiO (c) nanoparticles in stock solutions (Canli and Canli, 2020).
Figure 1 in Lethal and sublethal effects of exposure to Roundup 360 Plus for the Chaoborus flavicans larvae (Diptera: Chaoboridae)
Figure 1. The distribution of C. flavicans larvae within the water column under different concentrations of GLY. Box-mean, whisker-SD, n = 10, 0-close to the bottom, 1-in the water column, 2-close to the surface of the water. The letters above boxes indicate significant differences between time points (Tukey test, p <0.05)
Figure 2 in Lethal and sublethal effects of exposure to Roundup 360 Plus for the Chaoborus flavicans larvae (Diptera: Chaoboridae)
Figure 2. Morphological malformations of C. flavicans larvae. a– control organisms. Note two pairs of air sacs (arrows) and the digestive system (arrowhead). b– magnified picture of a pair of air sacs of a control insect. Note the regular distribution of chromatophores over the sacs. c– C. flavicans larva exposed to 20 µg/L GLY. Note altered pigmentation of the air sacs (arrow) and contortion of the body. d– C. flavicans larva exposed to 100 µg/L GLY. Note altered pigmentation, a contortion of the body that is close to the front air sacs (arrowhead), and darkening of the body. e, f– C. flavicans larva exposed to 400 µg/L GLY. Note the disappearance of pigmentation of air sacs, and the darkening of the body.
ScienceDex guides
Understand access before you commit
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.