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Figure 10 in All aspects of the toxic effects of lipopolysaccharide on rat liver and the protective effect of vitamin E and sodium selenite
Figure 10. Histological features of the apoptotic areas in the liver of the rats. A, B, C → Control; D, E, F → SS; G, H, I →VE; J, K, L → SS + VE; M, N, O → LPS; P, Q, R → LPS + SS; S, T, U, → LPS + VE; and V, W, X → LPS + SS + VE.
Figure 6 in All aspects of the toxic effects of lipopolysaccharide on rat liver and the protective effect of vitamin E and sodium selenite
Figure 6. Liver sections of the LPS + SS-treated rats. Showing (A) ⇑: dilation of the sinusoids, *: necrosis, and ►: vacuolar degeneration; and (B) ↑↑: vascular congestion and ⇒: hemorrhage at 200×.
Figure 4 in All aspects of the toxic effects of lipopolysaccharide on rat liver and the protective effect of vitamin E and sodium selenite
Figure 4. Liver sections of the LPS-treated rats. (A) Showing Δ: leukocyte infiltration, *: necrosis, Δ: dilation of the sinusoids at 200×; (B) ►: vacuolar degeneration, →: binucleated hepatocytes at 400×; (C) ⇒: hemorrhage, Δ: leukocyte infiltration, *: necrosis, ↑↑: vascular congestion; and (D) ⇑: dilation of the sinusoids and *: necrosis at 200×.
Figure 3 in All aspects of the toxic effects of lipopolysaccharide on rat liver and the protective effect of vitamin E and sodium selenite
Figure 3. Liver section of the control rats, CV: central vein at 200×. Histological structures (A, B) of the control, VE, SS, and VE + SStreated rats were similar to the control group.
Figure 2 in All aspects of the toxic effects of lipopolysaccharide on rat liver and the protective effect of vitamin E and sodium selenite
Figure 2. TEAC values (μmol of Trolox equiv/gram tissue) in the liver of rats treated with LPS (10 mg/kg bw), VE (200 mg/kg bw), and SS (0.35 mg/kg bw). Significance was accepted as P <0.05.
Figure 1 in All aspects of the toxic effects of lipopolysaccharide on rat liver and the protective effect of vitamin E and sodium selenite
Figure 1. FRAP values (μmol of FeII equiv/gram tissue) in the liver of rats treated with LPS (10 mg/kg bw), VE (200 mg/kg bw), and SS (0.35 mg/kg bw). Significance was accepted as P <0.05.
Figure 5 in Investigation of protective effects of lithium borate on spermatogenesis and testes histopathology against cadmium-induced acute toxicity in rats
Figure 5. Testes tissue, control and LTB groups, negative COX-2 expression (AC), Cd group, severe COX-2 expressions in damaged tubules and intertubular intervals (B), LTB + Cd group, mild COX-2 expression in interstitial tissue (arrowheads) (D), IHC - P, Bar: 20µm.
Figure 4 in Investigation of protective effects of lithium borate on spermatogenesis and testes histopathology against cadmium-induced acute toxicity in rats
Figure 4. Testes tissue, Control and LTB groups, negative 8-OHdG expression (AC), Cd group, severe cytoplasmic 8-OHdG expressions in spermatocytes and spermatogonium in damaged tubules (arrowheads) (B), LTB + Cd group, mild cytoplasmic 8-OHdG expression in spermatocytes (arrowheads) (D), IHC - P, Bar: 20 µm.
Figure 3. Negative Caspase-3 in Investigation of protective effects of lithium borate on spermatogenesis and testes histopathology against cadmium-induced acute toxicity in rats
Figure 3. Negative Caspase-3 expressions in testes tissues of control and LTB groups (A and C), severe Caspase-3 expression in spermatocytes of Cd group (arrowheads) (B), mild Caspase- 3 expression in spermatocytes (arrowheads) of LTB + Cd group (D), IHC - P, Bar: 20 µm.
Figure 1 in Investigation of protective effects of lithium borate on spermatogenesis and testes histopathology against cadmium-induced acute toxicity in rats
Figure 1. Testicular tissue, normal anatomical appearance (A), oedema, hyperaemia, congestion and haemorrhage (B), normal anatomical appearance (C), moderate oedematous and mild hyperaemic (D).
Figure 6 in Toxicity effects of copper on two species of marine diatoms microalgae and two species of dinoflagellates
Figure 6. Dynamics of organic carbon content, C (a), the Fv/Fm value (b) and the relative electronic transport rate, rETR on 3-ed day (c) in L. fissa at different copper ions concentrations: 1 – control, 2 – 3 µg·L-1, 3 – 5 µg·L-1, 4 – 10 µg·L-1, 5 – 50 µg·L-1, 6 – 100 µg·L-1, 7 – 200 µg· L-1. The average values of ± standard deviation are presented.
Figure 4 in Toxicity effects of copper on two species of marine diatoms microalgae and two species of dinoflagellates
Figure 4. Dynamics of organic carbon content, C (a, b), Fv/Fm (c) and relative electron transport rate, rETR on 3-ed day (d) in C. pelagica culture at different copper ions concentrations in small celled culture (a, c, d): 1 – control, 2 – 10 µg·L-1, 3 – 100 µg·L-1, 4 – 200 µg.L-1, 5 – 400 µg.L-1, 6 – 600 µg.L-1 and in large cell culture (b): 1 – control, 2 – 1 µg·L-1, 3 – 3 µg·L-1, 4 – 5 µg·L-1, 5 – 10 µg·L-1, 6 – 50 µg·L-1. The average values of ± standard deviation are presented.
Figure 2 in Toxicity effects of copper on two species of marine diatoms microalgae and two species of dinoflagellates
Figure 2. Relationship between microalgae optical density and organic carbon content (mg C· L-1) at a wavelength of 750 nm (OD750) in cultures: a – P. tricornutum, b – C. pelagica, c – P. nanum, d – L. fissa.
Figure 1 in Toxicity effects of copper on two species of marine diatoms microalgae and two species of dinoflagellates
Figure 1. View of microalgae cells under a light microscope: a – C. pelagica, b – P. tricornutum, c – L. fissa, d – P. nanum. The total magnification of the system is 400 times.
Figure 3 in Toxicity effects of copper on two species of marine diatoms microalgae and two species of dinoflagellates
Figure 3. Dynamics of organic carbon content, C (a, b), Fv/Fm (c, d) and the relative electronic transport rate, rETR on the 3rd day (e, f) in P. tricornutum at different copper ions concentrations: 1 – control, 2 – 1 µg·L-1, 3 – 5 µg·L-1, 4 – 10 µg·L-1, 5 – 50 µg·L-1, 6 – 100 µg·L-1, 7 – 200 µg·L-1; a, c, e – initial biomass of the culture is 0.2 mg C L-1, b, d, f – 1.0 mg C·L-1. The average values of ± standard deviation are presented.
Figure 5 in Toxicity effects of copper on two species of marine diatoms microalgae and two species of dinoflagellates
Figure 5. Dynamics of organic carbon content, C (a, b), Fv/Fm value (c, d) and relative electronic transport rate, rETR on 3-ed day (e, f) in P. nanum with an initial biomass of 0.5 mg C·L-1 (a, c, e) at copper ions concentrations: 1 – control, 2 – 1 µg·L-1, 3 – 3 µg·L-1, 4 – 5 µg·L-1, 5 – 10 µg·L-1, 6 – 50 µg· L-1, 7 – 100 µg·L-1 and with an initial biomass of 1.5 mg C.L-1 (b, d, f) at copper concentrations: 1 – control, 2 – 10 µg·L-1, 3 – 40 µg·L-1, 4 – 60 µg·L-1, 5 – 100 µg·L-1, 6 – 200 µg·L-1. The average values of ± standard deviation are presented.
Fig. 1 in Toxicity, repellency, and laboratory performance of consumer bait products for German cockroach (Blattodea: Ectobiidae) management
Fig. 1. Performance index (PI) relationships for German cockroach bait products and an untreated control determined in Ebeling choice boxes against 7 fieldcollected and 1 susceptible strain. Points represent means of 6 replicate boxes, each containing 20 adult male German cockroaches.
Fig. 3 in Toxicity for control of Frankliniella schultzei and Selenothrips rubrocinctus (Thysanoptera: Thripidae) of several common synthetic insecticides
Fig. 3. The bioassays to evaluate the toxicity of selected insecticides on common blossom thrips, Frankliniella schultzei, and red-banded thrips, Selenothrips rubrocinctus, were conducted in 90 mL plastic cups. Each cup had 10 thrips and a 3 cm long piece of insecticide-treated bean.
Fig. 1 in Toxicity for control of Frankliniella schultzei and Selenothrips rubrocinctus (Thysanoptera: Thripidae) of several common synthetic insecticides
Fig. 1. Adult Frankliniella schultzei. Photograph by Ittipon Bannakan, Insect Taxonomy Group, the Entomology and Zoology Division, Plant Protection Research and Development office, Department of Agriculture, Bangkok, Thailand.
Fig. 3 in Toxicicity and histological changes caused by insecticides in Spodoptera frugiperda (Lepidoptera: Noctuidae) eggs
Fig. 3. Spodoptera frugiperda eggs treated with methomyl novaluron at 72, 96, 120, and 144 h. (A, B) Embryo showing differentiated regions at 72 and 96 h (circle). (C) Embryo at 120 h showing cuticle (ct), midgut (td), and muscle (m) formation. (D) Embryo at 144 h showing muscle (m) and cuticle (ct) formation.
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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.