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Figure 2 in Determination of oxidative, genotoxic, and histopathologic effects of metal pollution on the fish fauna inhabiting Karasu River, Turkey
Figure 2. The erythrocytic nuclear abnormalities determined in the three fish species A) micronucleus (arrow) in C. capoeta, B) notched nucleus (arrow) in C. capoeta, C) binucleated nucleus (arrow) in A. mossulensis, D) kidney shaped nucleus (black arrows) and bud nucleus (red arrow) in A. mossulensis, E) lobed nucleus (arrow) in S. cephalus, F) Bud nucleus (arrow) in S. cephalus Giemsa.
Figure 6 in Infestation and effect of parasitic isopod Epipenaeon ingens ingens Nobili, 1906 on commercial shrimp species in the eastern Mediterranean: a case study of the population of brown shrimp Penaeus aztecus Ives, 1891
Figure 6. Box and Whisker plot representation of the negative effect of E. ingens ingens on the gonadal development of the female host shrimp P. aztecus.
Figure 5. Sentinel 3 in Marine mucilage in the Sea of Marmara and its effects on the marine ecosystem: mass deaths
Figure 5. Sentinel 3 imagery of the chlorophyll-a concentration in the study area on April 22, 2021.
Figure 3 in Marine mucilage in the Sea of Marmara and its effects on the marine ecosystem: mass deaths
Figure 3. Some dead species were collected during sampling. The orange circle indicates Atherina sp., and the yellow square indicates other affected species.
Figure 2 in Marine mucilage in the Sea of Marmara and its effects on the marine ecosystem: mass deaths
Figure 2. Regional map and sampling stations in the southern of Sea of Marmara (1: Misakça, 2: Şirinçavuş, 3: Narlı, 4: Tatlısu)
Figure 1 in Marine mucilage in the Sea of Marmara and its effects on the marine ecosystem: mass deaths
Figure 1. Mucilage aggregation examples on the water surface in the Sea of Marmara, a) on April 23, 2021, on the coast of Misakça and b) on May 25, 2021, in Erdek Harbor.
Figure 3 in Effects of Ni (II) p-hydroxybenzoate with caffeine on metabolic, antioxidant, and biochemical parameters of model insect Galleria mellonella L. (Lepidoptera: Pyralidae)
Figure 3. Effects of Ni (II) p-hydroxybenzoate with caffeine on ion levels of Galleria mellonella. Bars represent the means (± SD) of four replicates. Means followed by the same letter are not significantly different (p> 0.05).
Figure 1 in Effects of Ni (II) p-hydroxybenzoate with caffeine on metabolic, antioxidant, and biochemical parameters of model insect Galleria mellonella L. (Lepidoptera: Pyralidae)
Figure 1. Effects of Ni (II) p-hydroxybenzoate with caffeine on metabolic enzyme activity of Galleria mellonella. Bars represent the means (±SD) of four replicates. Means followed by the same letter are not significantly different (p> 0.05).
Figure 5 in Effect of urban habitats on colony size of ants (Hymenoptera, Formicidae) In memory of Professor A. A. Zakharov (Russian Academy of Sciences, Moscow)
Figure 5. Colony size of species per different geographic area. A – Crematogaster subdentata; B – Lasius neglectus.
Figure 4 in Effect of urban habitats on colony size of ants (Hymenoptera, Formicidae) In memory of Professor A. A. Zakharov (Russian Academy of Sciences, Moscow)
Figure 4. Colony size of 9 species of ants in several habitats of the same geographic area (calculated according to (A. Zakharov, 1978, 2015). A – Lasius fuliginosus; B – Camponotus vagus; C – Lasius emarginatus; D – Lasius niger; E – Formica cinerea; F - Dolichoderus quadripunctatus; G – Lasius brunneus; H – Crematogaster subdentata; I – Lasius neglectus.
Figure 2 in Effect of urban habitats on colony size of ants (Hymenoptera, Formicidae) In memory of Professor A. A. Zakharov (Russian Academy of Sciences, Moscow)
Figure 2. Calculated curve of the size of the ant colony by the intensity of movement of foragers per 1 min along the trail (counting only in one direction, Zakharov, 1979; 2015). Within 14–140 - according to A. Zakharov (1979), from 184 to 307 - our data, with an additional calculation formula in this range of values.
Figure 3 in Effect of urban habitats on colony size of ants (Hymenoptera, Formicidae) In memory of Professor A. A. Zakharov (Russian Academy of Sciences, Moscow)
Figure 3. Colony size in 21 ant species, calculated by the formula of A. Zakharov (1979; 2015). Ukraine: A – Kyiv region, deciduous (Kd) and coniferous (Kp) forests, natural habitats; B – Kyiv, suburban habitats (Ks); C – Kyiv city, urban habitats; D – natural habitats in Crimea (C1 – mountain steppes, C2 – mountain meadows) and in the Carpathians (Carp, mountain meadows); Crimea, steppe areas, natural habitats (C_aet); suburban and urban habitats in Crimea (L_neg, C_sub); Crimea, oak-pistachio-juniper forests, natural habitats (P_tau; F_gag; C_sch); Russian Federation: E, F – Rostov-on-Don, suburban (L_neg_R2) and urban (L_neg_R1; C_sub_R1) habitats; Uzbekistan: G – natural (riparian forests, C_sub_tu) and urban (Tashkent city, everything else) habitats; Russian Federation: H – Ural, natural habitats (taiga). Ant species: L_pla – Lasius platythorax; Dol – Dolichoderus quadripunctatus; L_ful – Lasius fuliginosus; L_ema – Lasius emarginatus; L_bru – Lasius brunneus; F_ruf – Formica rufa; L_nig – Lasius niger; F_cin – Formica cinerea; C_vag – Camponotus vagus; C_aet – Camponotus aethiops; F_tru – Formica truncorum; F_pol – Formica polyctena; L_neg – Lasius neglectus; F_pra – Formica pratensis; P_tau – Plagiolepis tauricus; F_gag – Formica gagates; C_sch – Crematogaster schmidti; C_sub – Crematogaster subdentata; M_ber – Myrmica bergi; P_pal – Plagiolepis pallescens; F_aqu – Formica aquilonia.
Figure 1. D in Effect of urban habitats on colony size of ants (Hymenoptera, Formicidae) In memory of Professor A. A. Zakharov (Russian Academy of Sciences, Moscow)
Figure 1. D Locations of the study. Ukraine: 1 – Crimea (the Main ridge of the Mountainous Crimea and the South Coast, Saki region), 2 – Kyiv and Kyiv region, 3 – Carpathians; Uzbekistan: 4 – Tashkent city, tugai forests; Russian Federation: 5 – Ural, 6 – Rostov-on-Don city and region. Habitats. a – natural, b – suburban, c – urban.
Figure 2 in Autophagic chemicals effect to Atg8 and rice stripe virus relative expressions, and Wolbachia relative density in Laodelphax striatellus (Hemiptera: Delphacidae)
Figure 2. Comparison of Atg8, Wolbachia, and RSV relative expressions and densities. Vertical bar lines indicate the ± of SD. Significant difference was determined by the Student's t-tests accompanied by Bonferroni correction (0.05). Control was used as a reference. Asterisks represent a significant difference in genes between treatment and control (*p <0.05).
Figure 1 in Autophagic chemicals effect to Atg8 and rice stripe virus relative expressions, and Wolbachia relative density in Laodelphax striatellus (Hemiptera: Delphacidae)
Figure 1. Comparison of Atg8, Wolbachia, and RSV relative expressions and densities. Vertical bar lines indicate the ± of SD. Significant difference was determined by the Student's t-tests accompanied by Bonferroni correction (0.05). Control was used as a reference. Asterisks represent a significant difference in genes between treatment and control (*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).
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.