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Figure 3 in Presence of larvae of lampreys, Lampetra sp. (Cephalaspidomorphi, Petromyzontiformes), in a French Catalan basin

Figure 3. – Neighbourg-Joining barcoding tree with the COI marker (642 bp) of European Lampetra spp. and Petromyzon marinus (94 specimens) iden- tifying the three ammocoetes caught at Nefiach. Numbers at nodes correspond to bootstrap values. Grey box refers to the complex [Lampetra fluviatilis + Lampetra planeri].

opencc-by-4.0Dec 2018View details →
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Figure 1 in Presence of larvae of lampreys, Lampetra sp. (Cephalaspidomorphi, Petromyzontiformes), in a French Catalan basin

Figure 1. – The Têt River in the Pyrénées-Orientales department and the lamprey location at Nefiach (square).

opencc-by-4.0Dec 2018View details →
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Figure 2. – A in Presence of larvae of lampreys, Lampetra sp. (Cephalaspidomorphi, Petromyzontiformes), in a French Catalan basin

Figure 2. – A: Three of the six lamprey larvae, or ammocoetes, belonging to the genus Lampetra caught in the Têt River at Nefiach (MNHN 2016-0363). B, C: Enlargement of the head and tail showing the absence of pigmentation respectively on the snout and on the extremity of the caudal fin (arrows). Scale bars = 1 cm.

opencc-by-4.0Dec 2018View details →
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Fig. 1 in Molecular identification and epidemiological data of Anisakis spp. (Nematoda: Anisakidae) larvae from Southeastern Pacific Ocean off Peru

Fig. 1. Scanning electron micrographs of Anisakis type I and II.1a and 2a. Cephalic end. Detail of the structures: oral cavity (oc), tooth (t), excretory pore (ep), subventral lip bulge (s). 1b. caudal end of Anisakis pegreffii. 2b. caudal end of Anisakis physeteris. Detail of the structures: anal pore (ap), mucron (m).

opencc-by-4.0Dec 2021View details →
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Fig. 2 in Molecular identification and epidemiological data of Anisakis spp. (Nematoda: Anisakidae) larvae from Southeastern Pacific Ocean off Peru

Fig. 2. Phylogenetic tree based on mtDNA cox2 gene sequences exploring the relationships among Anisakis species. The relationship was drawn using Bayesian inference (BI) and maximum likelihood (ML) methods. Posterior probability value (first) and nodal support is shown as bootstrap value (second) on the basis of 10 million generations for BI and 1000 replicates (only bootstrap values greater than 80% are shown) for ML, respectively. Scale bar indicate nucleotide substitutions per site. GenBank accession numbers are shown in parentheses. Hysterothylacium deardorffoverstreetorum was used as an outgroup.

opencc-by-4.0Dec 2021View details →
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Fig. 3 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 3. Visualization of fat reserves in the bone marrow of femur (row 1), knee joint (row 2), vertebral canal (row 3), orbital cavity (row 4), and heart surface (row 5). The three categories used are illustrated from left to right: clearly visible white and stiff fat (+); low amounts of visible fat with a soft consistency (+÷); absence of visible fat (serous adipose atrophy) (÷). All figures are from wild reindeer calves killed on Hardangervidda in spring 2015, except for the heart to the bottom right which is from a moose that died from winter starvation.

opencc-by-4.0Aug 2021View details →
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Fig. 6 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 6. Photograph from the inside of the skin showing Hypoderma tarandi larvae removed from the lower part of the back of a calf killed on Hardangervidda in spring 2015.

opencc-by-4.0Aug 2021View details →
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Fig. 9 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 9. Calculated mean air temperature (◦C) in the main summer pasture area of the Hardangervidda wild reindeer population for individual summers (June–August) 1989–2018. The summers of 2014 and 2015 are marked with a black circle. The dotted horizontal line shows the mean (7.4 ◦C) for the 30- year-period.

opencc-by-4.0Aug 2021View details →
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Fig. 5 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 5. Cephenemyia trompe larvae in the pharynx/nasopharynx of a calf killed on Hardangervidda in spring 2015. Note the paired, swollen retropharyngeal lymph nodes (Ln).

opencc-by-4.0Aug 2021View details →
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Fig. 4 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 4. Translucent white first stage Cephenemyia trompe larvae (1 mm) in the nasal mucosa of a calf killed on Hardangervidda in autumn 2014.

opencc-by-4.0Aug 2021View details →
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Fig. 10 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 10. Calculated number of summer days (June–August) with a mean air temperature ≥12 ◦C in the main summer pasture area of the wild reindeer population on Hardangervidda. The figure shows the mean and range for the 30-year period 1989–2018, and the mean for individual years 2014 and 2015 as well as for the five years with a higher mean temperature than in 2014.

opencc-by-4.0Aug 2021View details →
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Fig. 8 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 8. Group of adult hair-thin, about 3–5 cm long Elahostrongylus rangiferi nematodes in the muscle fascia of a calf killed on Hardangervidda in spring 2015.

opencc-by-4.0Aug 2021View details →
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Fig. 1 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 1. Map of southern Norway showing the location of the 24 Norwegian wild tundra reindeer populations. The Hardangervidda population (No. 16) is marked with brighter tan.

opencc-by-4.0Aug 2021View details →
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Fig. 2 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 2. Kernel Density Analysis, visualizing the main pasture area of radio-collared females in the wild reindeer population in Hardangervidda during June, July, and number of GPS positions recorded. Calculated center at UTM 32V: 426706–6650377 and average altitude at 1283m. The center in the previously used summer area with an asterisk. The red lines represent summer trails for hikers marked by the Norwegian Tourist Association. (For interpretation of the references to color in this figure of this article.)

opencc-by-4.0Aug 2021View details →
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Fig. 7 in High winter loads of Oestrid larvae and Elaphostrongylus rangiferi are associated with emaciation in wild reindeer calves

Fig. 7. Verminous pneumonia in a calf killed on Hardangervidda in spring 2015. Numerous confluent granulomas containing Elaphostrongylus rangiferi eggs and hatched first stage larvae. Haematoxylin and eosin stain. Bar, 100 μm.

opencc-by-4.0Aug 2021View details →
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Fig. 3 in Distribution, prevalence and intensity of moose nose bot fly (Cephenemyia ulrichii) larvae in moose (Alces alces) from Norway

Fig. 3. The predicted parasite intensity of moose nose bot fly larvae for harvested calves (red), yearlings (blue) and adult (green) moose in central and southern Norway. Predictions from the highest ranked intensity model with study area and age group. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

opencc-by-4.0Aug 2021View details →
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Fig. 2 in Distribution, prevalence and intensity of moose nose bot fly (Cephenemyia ulrichii) larvae in moose (Alces alces) from Norway

Fig. 2. The predicted infection prevalence of moose nose bot fly larvae with increasing moose (host) density. The shaded area shows the 95% confidence interval. Predictions from the highest ranked model with moose density. In the plot we used the function "jitter" in the R package ggeffects (Lüdecke, 2018), which adds small random variation to the data points to better reflect the amount of data for moose densities. Hence, the points do not reflect exact values as they are binomial.

opencc-by-4.0Aug 2021View details →
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Fig. 1 in Distribution, prevalence and intensity of moose nose bot fly (Cephenemyia ulrichii) larvae in moose (Alces alces) from Norway

Fig. 1. Study areas in southern (Oslo, AurskogHøland and Kongsvinger) and central Norway (Selbu, Tydal, Malvik, Stjørdal and Meråker) with location and moose density (moose density, see Materials and methods) in sampling municipalities. Red filled circle indicate where the moose nose bot fly (Cephenemyia ulrichii) was first found in Norway, and open circles show where moose heads were examined without detection of the moose nose bot fly in 1987 (Nilssen and Haugerud, 1994). Blue circles indicate where the moose nose bot fly were found in Sweden in the late 1970s and 1980s (Steen et al., 1988). (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

opencc-by-4.0Aug 2021View details →
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Fig. 4 in Influence of rainfall regime in the Cerrado biome on the maintenance of traps built by Myrmeleon brasiliensis (Navás) (Neuroptera: Myrmeleontidae) larvae and the morphology of adults

Fig. 4. Size (mean ± SD) of Myrmeleon brasiliensis (Návas) larvae traps submitted to different rain freQuencies. (Treatment I: control, no rain; Treatment II: rain every 10 days and Treatment III: rain every 5 days).

opencc-by-4.0Nov 2022View details →
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Fig. 3 in Influence of rainfall regime in the Cerrado biome on the maintenance of traps built by Myrmeleon brasiliensis (Navás) (Neuroptera: Myrmeleontidae) larvae and the morphology of adults

Fig. 3. Percentage of live larvae, pupae, live adults and dead larvae of Myrmeleon brasiliensis (Návas, 1914) (Neuroptera: Myrmeleontidae) observed at the end of the experiments (Treatment I: control, without rain; Treatment II: rain every 10 days and Treatment III: rain every 5 days).

opencc-by-4.0Nov 2022View details →

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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.

allen-brain-atlas
neuroscienceopenDocumentation, web resources, and API references are available online.
Last verified 2026-04-30Open record

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.

abode-home-cage
behavioral-neuroscienceopenThe DataShare record exposes download links for annotations, documentation, license text, and the zipped per-snippet data directory.
Last verified 2026-04-30Open record

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.

dandi-nwb
electrophysiologyopenPublished Dandiset metadata and archive endpoints are available through the production DANDI API.
Last verified 2026-04-30Open record

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.

ibl
behavioral-neuroscienceopenPublic sessions can be searched and loaded from the IBL public data server through ONE.
Last verified 2026-04-29Open record

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.

openneuro
neuroscienceopenPublished datasets are available on demand over the internet.
Last verified 2026-04-29Open record