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Fig. 6 in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 6 - Philoctetes delvarei Tussac & Tussac, male, holotype: A) habitus, dorsal view; B) habitus, lateral view; C) head, frontal view; D) T3, dorso-lateral view.
Fig. 4 in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 4 - Philoctetes putoni (du Buysson), female: A) habitus, dorsal view; B) habitus, lateral view; C) head, frontal view; D) T3, dorso-lateral view.
Fig. 7 - A,C,E in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 7 - A,C,E) Philoctetes helveticus (Linsenmaier), female: A) mesosoma, dorsal view; C) mesoscutum, propodeum and T1, lateral view; E) T1, dorsal view. B,D,F) Philoctetes putoni (du Buysson), female: B) mesosoma, dorsal view; D) mesoscutum, propodeum and T1, lateral view; F) T1, dorsal view.
Fig. 3 - A in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 3 - A) Philoctetes helveticus, female (Photo by M. Jacobs); B) Aosta Valley, Chamolé lake, 2350 m (Photo by C. Monte); C) O. Niehuis looking for P. putoni at Milefonts, 2030 m, Mercantour National Park (Photo by P. Rosa).
Fig. 2 in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 2 - Philoctetes helveticus (Linsenmaier), male: A) habitus, dorsal view; B) habitus, lateral view; C) scutellum and metascutellum, lateral view; D) T3, dorso-lateral view.
Fig. 1 in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 1 - Philoctetes helveticus (Linsenmaier), female: A) habitus, dorsal view; B) habitus, lateral view; C) head, frontal view; D) T3, dorso-lateral view.
Fig. 5 in Notes on endemic Alpine chrysidids, with key to Alpine Philoctetes Abeille de Perrin, 1879, and remarks on two rarely collected species (Hymenoptera, Chrysididae)
Fig. 5 - Philoctetes putoni (du Buysson), female, holotype: A) habitus, dorsal view; B) habitus, lateral view; D) T3, dorso-lateral view; C) Philoctetes putoni (du Buysson), male: genital capsula.
Figure 2 in Third record of the Critically Endangered Brazilian Merganser Mergus octosetaceus in São Paulo state, south-east Brazil, after almost two centuries
Figure 2. Locality where observations were made in August and November 2017, rio Claro, Salesópolis, São Paulo, Brazil (Miguel Nema Neto)
Figure 1 in Third record of the Critically Endangered Brazilian Merganser Mergus octosetaceus in São Paulo state, south-east Brazil, after almost two centuries
Figure 1. Male Brazilian Merganser Mergus octosetaceus, rio Claro, Salesópolis, São Paulo, Brazil, 25 August 2017 (Fabiana Dias Pereira)
Figure 1 in Herbicide response and germination behavior of two goosegrass (Eleusine indica) populations in the Australian environment
Figure 1. Effect of paraquat dose on (A) seedling survival, (B) spike number (percent of nontreated control), and (C) aboveground biomass (percent of nontreated control) of the two Australian populations (Gatton and Ingham) of Eleusine indica. Error bars represent the standard error of the mean.
Figure 5 in Herbicide response and germination behavior of two goosegrass (Eleusine indica) populations in the Australian environment
Figure 5. Effect of osmotic potential on the germination of the two Australian populations (Gatton and Ingham) of Eleusine indica incubated under alternating light/ dark for 28 d at 30/20 C.The lines represent a three-parameter sigmoid model fit to the germination data in response to concentrations of osmotic potentials.
Figure 3 in Herbicide response and germination behavior of two goosegrass (Eleusine indica) populations in the Australian environment
Figure 3. Effect of light/dark regimes on the germination of the two Australian populations (Gatton and Ingham) populations of Eleusine indica. Seeds were incubated for 28 d at alternating day/night temperatures of 30/20 C. Error bars represent the LSD at the 5% level of significance.
Figure 4 in Herbicide response and germination behavior of two goosegrass (Eleusine indica) populations in the Australian environment
Figure 4. Effect of sodium chloride concentration on the germination of the two Australian populations (Gatton and Ingham) of Eleusine indica incubated under alternating light/dark for 28 d at 30/20 C.The lines represent a three-parameter logistic model fit to the germination data in response to sodium chloride concentrations.
Figure 2 in Herbicide response and germination behavior of two goosegrass (Eleusine indica) populations in the Australian environment
Figure 2. Effect of alternating day/night temperatures (15/5 to 35/25 C) on the germination of the two Australian populations (Gatton and Ingham) of Eleusine indica. Error bars represent the LSD at the 5% level of significance.
Fig. 6 in Seasonal response of benthic foraminifera to anthropogenic pressure in two stations of the Gulf of Trieste (northern Adriatic Sea, Italy): the marine protected area of Miramare versus the Servola water sewage outfall
Fig. 6: Rank-frequency diagram for the Ser(a) and Res(b) stations using the cumulative abundance (as relative frequency) for y-axe and the decreasing rank order for x-axe of each species for each sample. Both axes are on logarithmic scale.
Fig. 4 in Seasonal response of benthic foraminifera to anthropogenic pressure in two stations of the Gulf of Trieste (northern Adriatic Sea, Italy): the marine protected area of Miramare versus the Servola water sewage outfall
Fig. 4: Foraminiferal data for Ser and Res stations using the complete living assemblage of the 0-2 cm level: a) Foraminiferal density (FD) as the number of specimens normalised to 50 cc of sediments and species richness; b) Dominance index; c) bias corrected Shannon (H' bc) and the exponential function Exp(H' ) indexes.
Fig. 3 in Seasonal response of benthic foraminifera to anthropogenic pressure in two stations of the Gulf of Trieste (northern Adriatic Sea, Italy): the marine protected area of Miramare versus the Servola water sewage outfall
Fig. 3: Potentially toxic elements (PTE) concentration in the Ser (a) and Res (b) stations calculated for the 0-1 cm level. PTEs are expressed in micrograms per gram (µg/g).
Fig. 1 in Seasonal response of benthic foraminifera to anthropogenic pressure in two stations of the Gulf of Trieste (northern Adriatic Sea, Italy): the marine protected area of Miramare versus the Servola water sewage outfall
Fig. 1: Study area and location of the Ser (Servola) and Res (Riserva Naturale Marina di Miramare) stations. The Servola pipeline is evidenced in the enlarged square.
Fig. 5 in Effects of ocean acidification on phenology and epiphytes of the seagrass Posidonia oceanica at two CO vent systems of Ischia (Italy) Abstract
Fig. 5: Temporal evolution of the coverage percentage of the epiphytic assemblages (June, August, and October) at the studied stations.
Fig. 6 in Effects of ocean acidification on phenology and epiphytes of the seagrass Posidonia oceanica at two CO vent systems of Ischia (Italy) Abstract
Fig. 6: Non-metric multidimensional scaling (nMDS) plot of the epiphytic assemblages: a) June (stress = 0.16); b) August (stress = 0.15); c) October (stress = 0.12); d) three months plotted together (stress = 0.25) to highlight the evolution of the community over time. Circles indicate N3, empty triangles indicate Vu3; inverse filled triangles indicate Vu6; quadrats identify the control (NC). Colors indicate sampling month: black = June; dark gray = August; and light gray = October.
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.