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Figure 2 in The impact of chilling on selected attributes of the blowfly, Calliphora vicina (Robineau-Desvoidy, 1830) (Diptera: Calliphoridae), under laboratory conditions
Figure 2. Effect of chilling period on the larval (a) and pupal (b) development durations of Calliphora vicina.
Figure 4 in New insights on the impact of earthworm extract on the growth of beneficial soil fungi: species-specific alteration of the nematophagous fungal growth and limitation of an entomopathogenic fungus
Figure 4. Growth of Purpureocillium lilacinum after 20 days postexposer to two different earthworm based media: fresh earthworms (FE) (four concentration C1, C2, C3, and C4), and earthworms devoid of gut contents (EDG) (four concentration C1, C2, C3, and C4), C1 = 40 g/L, C2 = 20 g/L, C3 = 10 g/L, C4 = 5 g/L, and two rich media: potato dextrose agar (PDA), and brain heart infusion (BHI).
Figure 5 in New insights on the impact of earthworm extract on the growth of beneficial soil fungi: species-specific alteration of the nematophagous fungal growth and limitation of an entomopathogenic fungus
Figure 5. Evaluation of conidial germination of the fungus Beauveria bassiana exposed to two different earthworm extracts: fresh earthworms (FE) and earthworms without gut contents, EDG, and two conventional media: potato dextrose agar (PDA), and brain heart infusion agar (BHI). A. Percentage germination on conventional and earthworm-based media. B. Percent germination as a function of concentration and earthworm-based medium. Concentrations are equivalent to C1 = 40 g/L, C2 = 20 g/L, C3 = 10 g/L, and C4 = 5 g/L. Results of one-way ANOVA (A) or two-way ANOVA (B), and differences are significant according to Tukey's test (HSD) and groups "a", "b" and "c".
Figure 3 in New insights on the impact of earthworm extract on the growth of beneficial soil fungi: species-specific alteration of the nematophagous fungal growth and limitation of an entomopathogenic fungus
Figure 3. Evaluation of vegetative growth, conidial production and germination in the fungus Purpureocillium lilacinum exposed to two earthworm extracts: fresh earthworm (FE), earthworms devoid of intestinal contents (EDG) and two conventional media: potato dextrose agar (PDA), and brain heart infusion agar (BHI). A. Cumulative growth from 3 to 18 days according to conventional and earthworm-based media. B. Cumulative growth as a function of concentration and earthworm-based medium. C. Conidia production (×10⁵ conidia/mL) according to conventional and earthworm-based media. D. Conidia production (×10⁵ conidia/mL) according to concentration and earthworm-based medium. E. Percent germination on conventional and earthworm-based media. F. Percent germination as a function of concentration and earthworm-based medium. Concentrations are equivalent to C1 = 40 g/L, C2 = 20 g/L, C3 = 10 g/L, and C4 = 5 g/L. Results of one-way ANOVA (A, C, E) or two-way ANOVA (B, D, F), and differences are significant at Tukey's test (HSD) and groups "a", "b" and "c".
Figure 1 in New insights on the impact of earthworm extract on the growth of beneficial soil fungi: species-specific alteration of the nematophagous fungal growth and limitation of an entomopathogenic fungus
Figure 1. Evaluation of vegetative growth, conidial production and germination in the fungus Arthrobotris musiformis exposed to two earthworms' extracts: fresh earthworm (FE), earthworms devoid of intestinal contents (EDG) and two conventional media: potato dextrose agar (PDA), and brain heart infusion agar (BHI). A. Cumulative growth from 3 to 18 days according to conventional and earthworm-based media. B. Cumulative growth as a function of concentration and earthworm-based medium. C. Conidia production (×10⁵ conidia/mL) according to conventional and earthworm-based media. D. Conidia production (×10⁵ conidia/mL) according to concentration and earthworm-based medium. E. Percent germination on conventional and earthworm-based media. F. Percent germination as a function of concentration and earthworm-based medium. Concentrations are equivalent to C1 = 40 g/L, C2 = 20 g/L, C3 = 10 g/L, and C4 = 5 g/L. Results of one-way ANOVA (A, C, E) or two-way ANOVA (B, D, F), and differences are significant at Tukey's test (HSD) and groups "a", "b" and "c".
Figure 9 in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 9. Flooded burnt areas near the island of Vranjina in the northern part of Lake Skadar/Shkodra (photographed on October 3, 2020). Photo by V. Pešić.
Figure 8 in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 8. Burnt areas (brown patches) resulted from wildfires southeastward of Lake Šas are shown for (a) 11 September, (b) 13 September and (c) 21 September 2020 (MSI Sentinel-2). Yellow arrow shows zoom on the selected area marked by yellow square.
Figure 5 in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 5. The suspended particulate matter oncentration (SPM, g/m3) in Lake Šas on (a) 11 September 2020, 09:40 GMT, MSI Sentinel-2B; (b) 13 September 2020, 09:30 GMT, MSI Sentinel-2A; (c) 21 September 2020, 09:40 GMT, MSI Sentinel-2B; (d) 8 October 2020, 09:30 GMT, MSI Sentinel-2B. The River Bojana/Buna passes in the southeastern corner of the frame.
Figure 7 in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 7. Burnt areas (brown patches) resulted from wildfires northwestward of Lake Skadar/Shkodra are shown for (a) 29 August, (b) 13 September and (c) 21 September 2020 (MSI Sentinel-2). Yellow arrows show zoom on three selected areas marked by yellow squares.
Figure 6. The Chlorophyll-a in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 6. The Chlorophyll-a concentration (Chla, mg/m3) in Lake Šas on (a) 11 September 2020, 09:40 GMT, MSI Sentinel-2B; (b) 13 September 2020, 09:30 GMT, MSI Sentinel-2A; (c) 21 September 2020, 09:40 GMT, MSI Sentinel- 2B; (d) 8 October 2020, 09:30 GMT, MSI Sentinel-2B. The River Bojana/Buna passes in the southeastern corner of the frame.
Figure 1 in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 1. Satellite image (OLI Landsat-8) of Lake Skadar/Shkodra area on 20 September 2020. Red squares show two areas (the northern and southern) of special interest of the impact of wildfires (white smokes) on the environment. Small red square shows location of Lake Šas.
Figure 2 in The impact of wildfires on the Lake Skadar/Shkodra environment
Figure 2. The true color satellite imagery of Lake Skadar/Shkodra environment on (a) 11 September 2020, 09:40 GMT, MSI Sentinel-2B; (b) 16 September 2020, 09:40 GMT, MSI Sentinel-2A; (c) 21 September 2020, 09:40 GMT, MSI Sentinel-2B; (d) 8 October 2020, 09:30 GMT, MSI Sentinel-2B.
Figure 4 in River degradation impacts fish assemblages in Kosovo's Ibër basin
Figure 4. Left: CCA results between physico-chemical variables and species densities. Right: CCA results between anthropogenic pressures and species densities.
Figure 1 in River degradation impacts fish assemblages in Kosovo's Ibër basin
Figure 1. Site locations on the Ibër and its tributaries in northern Kosovo; inset map shows locations on the Ibër's main western stem, upstream of the city of Mitrovica. Minor inset map (upper left) shows the position of Kosovo in the Western Balkans (data about sampling sites presented in Table 2).
Figure 3 in River degradation impacts fish assemblages in Kosovo's Ibër basin
Figure 3. Left: MDS for sampling sites of Ibër river, regarding the physico-chemical variables. Red square: very polluted; Brown triangle: Polluted; Orange triangle: Less polluted. Right: MDS for sampling sites of Ibër river, regarding the anthropogenic pressures as recorded in the on-site protocol assessment.
Figure 2 in River degradation impacts fish assemblages in Kosovo's Ibër basin
Figure 2. Fish specimens photographed in the field aquarium during the survey: A. Squalius cephalus, B. Cobitis elongatoides, C. Phoxinus sp., D. Gobio obtusirostris, E. Rutilus rutilus, F. Salmo cf. trutta, G. Sabanejewia balcanica, H. Chondrostoma nasus, I. Romanogobio uranoscopus, and J. Barbus balcanicus. Photographs by Stamatis Zogaris.
Figure 8 in Impact of aquatic habitat environment on the elemental composition and shell shape variability of the Beringian freshwater mussel Beringiana beringiana (Bivalvia, Unionidae)
Figure 8. Relationships between values of distribution coefficients (Kd Shell/Water Zn (A), Kd Shell/Water Sr (B) and Kd Shell/Water Al (C)) and principal component 1, revealed from the shell shape analysis of Beringiana beringiana. For the numbers of localities see caption for Figure 7.
Figure 6. Normed PCA factorial graph F1 in Impact of aquatic habitat environment on the elemental composition and shell shape variability of the Beringian freshwater mussel Beringiana beringiana (Bivalvia, Unionidae)
Figure 6. Normed PCA factorial graph F1 × F2 of two revealed geographical groups of Beringiana beringiana samples (blue circles indicate samples from Primorsky Krai, Kunashir, Sakhalin, and Iturup islands; red circles indicate samples from Kamchatka Peninsula). Ellipses show 95 % confidence interval.
Figure 5 in Impact of aquatic habitat environment on the elemental composition and shell shape variability of the Beringian freshwater mussel Beringiana beringiana (Bivalvia, Unionidae)
Figure 5. Relationships between Kd Shell/Sediment Al and Kd Shell/Water Al: (1) Peschanoye Lake, Kunashir Island, (2) Bolshoye Vavayskoye Lake, Sakhalin Island, (3) Vaskovskoye Lake, Primorsky Krai, (4) Lebedinoe Lake, Iturup Island, (5) Kurazhechnoye Lake, Kamchatka Peninsula, (6) Khalaktyrskoye Lake, Kamchatka Peninsula, (7) Chernoye Lake, Sakhalin Island.
Figure 4 in Impact of aquatic habitat environment on the elemental composition and shell shape variability of the Beringian freshwater mussel Beringiana beringiana (Bivalvia, Unionidae)
Figure 4. Median joining networks of Beringiana beringiana (N = 50) based on the COI gene fragment. The circle size is proportional to the number of available sequences belonging to the given haplotype (the smallest = 1 sequence). The red numbers near branches indicate the number of nucleotide substitutions between haplotypes.
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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.