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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 1 in Using of fluctuating asymmetry in adult Pelophylax ridibundus (Amphibia: Anura: Ranidae) meristic traits as a method for assessing developmental stability of population and environmental quality of their habitat: industrial area in southern Bulgaria
Figure 1. An indicative map of the sites in southern Bulgaria where P. ridibundus individuals were captured in 2019.
Figure 2 in Using of fluctuating asymmetry in adult Pelophylax ridibundus (Amphibia: Anura: Ranidae) meristic traits as a method for assessing developmental stability of population and environmental quality of their habitat: industrial area in southern Bulgaria
Figure 2. Photos of some asymmetric P. ridibundus individuals from site 1: the Chaya River in southern Bulgaria. Legend: a–d: asymmetric morphological traits on the back of the body and hind limbs of frogs, e–f: asymmetric morphological traits on the fingers of frogs. Trait 1 – number of stripes on the dorsal side of the thigh (femur); trait 2 – number of spots on the dorsal side of the thigh; trait 3 – number of stripes on the dorsal side of the shank (crus); trait 4 – number of spots on the dorsal side of the shank; trait 5 – number of stripes on the foot (pes); trait 6 – number of spots on the foot; trait 7 – number of stripes and spots on the back (dorsum); trait 8 – number of white spots on the ventral side of the second finger of the hind leg; trait 9 – number of white spots on the ventral side of the third finger of the hind leg; trait 10 – number of white spots on the ventral side of the fourth finger of the hind leg.
Fig. 7 in Temporal dynamics of fruit-feeding butterflies (Lepidoptera: Nymphalidae) in two habitats in a seasonal Brazilian environment
Fig. 7. Non-metric multidimensional scaling based on the Nymphalidae species composition captured in 4 climatic periods—wet (dark blue), dry (red), transition from wet to dry (T.wd, light blue), and transition from dry to wet (T.dw, black)—in 2 habitats, savanna (S) and gallery forest (F) in the Fazenda Água Limpa and the Reserva Ecológica do Roncador, Brasília, DF. A.dem, Archeoprepona demophon; M.hel, Morpho helenor; and P.pol, Pariphthimoides poltys best characterize the T.dw, whereas C.aco, Catonephele acontius; P.oci, Pareupthichia ocirrhoe; and T.lao, Temenis laothoe best characterize the T.wd. Stress: 0.15.
Fig. 6 in Temporal dynamics of fruit-feeding butterflies (Lepidoptera: Nymphalidae) in two habitats in a seasonal Brazilian environment
Fig. 6. Pielou's evenness values of the Nymphalidae species in the dry and wet seasons and in the transitional periods between these 2 seasons,from wet to dry (T.wd) and from dry to wet (T.dw), in savanna (Cerrado sensu stricto, ss) and forest (gallery forest) habitats in the Fazenda Água Limpa and the Reserva Ecológica do Roncador, Brasília, DF. Different lowercase letters represent significant differences (P <0.05).
Fig. 4. A in Temporal dynamics of fruit-feeding butterflies (Lepidoptera: Nymphalidae) in two habitats in a seasonal Brazilian environment
Fig. 4. A) Temporal variation in Nymphalidae abundance captured in the dry and wet seasons and in the 2 transitional periods between those seasons, from wet to dry (T.wd) and from dry to wet (T.dw), in savanna (Cerrado sensu stricto, ss) and forest (gallery forest) habitats of the Fazenda Água Limpa and the Reserva Ecológica do Roncador, Brasília, DF. The box plots show the differences between the 4 climatic periods, considering B) the total butterfly abundance (gallery forest + savanna), and that C) in the gallery forest and D) in the savanna separately. Different lowercase letters represent significant differences (P <0.05).
Fig. 3 in Temporal dynamics of fruit-feeding butterflies (Lepidoptera: Nymphalidae) in two habitats in a seasonal Brazilian environment
Fig. 3. Circular analysis of the number of individuals reflecting the abundance of the different Nymphalidae subfamilies and tribes captured from Jul 2012 to Jun 2013 in the Fazenda Água Limpa and Reserva Ecológica do Roncador. In this analysis, each column's length represents the observed abundance and the arrow the tendency of the highest abundance.
Fig. 2 in Temporal dynamics of fruit-feeding butterflies (Lepidoptera: Nymphalidae) in two habitats in a seasonal Brazilian environment
Fig. 2. Circular analysis of the number of individuals reflecting the abundance of Nymphalidae captured from Jul 2012 to Jun 2013 in the Fazenda Água Limpa and Reserva Ecológica do Roncador. In this analysis, each column's length represents the observed abundance and the arrow the tendency of the highest abundance.
Fig. 1. Rarefaction curves, generated with 1,000 in Temporal dynamics of fruit-feeding butterflies (Lepidoptera: Nymphalidae) in two habitats in a seasonal Brazilian environment
Fig. 1. Rarefaction curves, generated with 1,000 randomizations without replacement, based on the MauTau (Sobs, black circles) and "total" estimated (Jackknife 1, gray circles) values. The data of Nymphalidae species richness was acquired from Jul 2012 to Jun 2013 in the Fazenda Água Limpa and the Reserva Ecológica do Roncador, Brasilia, DF.
Figure 5 in Ecological and faunistic features of caddisflies (Insecta: Trichoptera) in different types of habitats in the Dinaric karst area (Central Croatia)
Figure 5. Maximum likelihood (ML) phylogram based on 658 bp long fragment of the mt COI DNA barcode region showing the relationships between species of the genus Setodess. Numbers above the branches represent bootstrap support (BS) for Neighbor-Joining (NJ) and ML analysis (NJ/ML). BS values less than 60 are not shown. Specimen ID from sequences obtained in this study are written with bold letters.
Figure 3 in Ecological and faunistic features of caddisflies (Insecta: Trichoptera) in different types of habitats in the Dinaric karst area (Central Croatia)
Figure 3. NMDS similarity analysis of caddisflies fauna at the study area (sampling sites correspond to the list in Tab. 1).
Figure 2 in Ecological and faunistic features of caddisflies (Insecta: Trichoptera) in different types of habitats in the Dinaric karst area (Central Croatia)
Figure 2. Dobra - spring (D1), Dobra - upper Dobra (D2), Dobra - canyon (D4), Kamačnik - spring (K1), Zagorska Mrežnica - spring (ZM), Sabljaci - reservoir (SR).
Figure 2. Hot spring habitats and a in Dragonflies from hot springs in Russia with a country-level checklist of species known to occur in geothermal environments
Figure 2. Hot spring habitats and a live dragonfly on the Kunashir Island. (A) Neskuchensky hot springs, a habitat of Sympetrum pedemontanum elatum, Anotogaster sieboldii, and Orthetrum melania, 26 July 2011. (B) Stolbovsky hot springs, a habitat of Mnais costalis, Anotogaster sieboldii, and Orthetrum melania, 29 July 2011. (C) Male of Orthetrum melania near the Neskuchensky hot springs, 26 July 2011. (Photos: Yu. S. Kolosova [A, C] and O. V. Aksenova [B]).
Figure 3 in First record of scalloped hammerhead shark Sphyrna lewini (Carcharhiniformes: Sphyrnidae) in freshwater habitat
Figure 3. Another side of S. lewini on 6 April 2020 in Mahakam river at Muara Baroh village, Muara Pahu subdistrict, Kutai Barat district, East Kalimantan province (Photo: Yuni Sri Wahyuni).
Figure 1 in First record of scalloped hammerhead shark Sphyrna lewini (Carcharhiniformes: Sphyrnidae) in freshwater habitat
Figure 1. Location of known S. lewini in Borneo. Yelow circles are S. lewini recorded in Bornean waters after Last et al. (2010), and red circle is recent inland record from Mahakam river, East Kalimantan province.
Figure 4 in Modeling habitat suitability and current distribution of the Maghreb magpie (Pica mauritanica)
Figure 4. (A) Current distribution of the Maghreb magpie in North Africa, (B) binary map of habitat suitability with a threshold> 0.6.
Figure 6 in Modeling habitat suitability and current distribution of the Maghreb magpie (Pica mauritanica)
Figure 6. Response curves of the explanatory variables included in the species distribution model (SDM) for Pica mauritanica. (MTWQ: mean temperature of wettest quarter).
Figure 5 in Modeling habitat suitability and current distribution of the Maghreb magpie (Pica mauritanica)
Figure 5. Two-dimensional plots of Pica mauritanica niche hypervolume with the most influential variables.
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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.