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Fig. 3 in Development of in-country live food production for amphibian conservation: The Mountain Chicken Frog (Leptodactylus fallax) on Dominica, West Indies
Fig. 3. (A) Two rows of cricket breeding containers and cockroach breeding bins below. (B) Inside of a cricket breeding container, including refugia, food items, and several egg laying containers, transplanted into an empty container to allow eggs to hatch. (C) Inside view of a cockroach breeding bin, including substrate, refugia, and several food items. Photos: D. Nicholson.
Fig. 2 in Development of in-country live food production for amphibian conservation: The Mountain Chicken Frog (Leptodactylus fallax) on Dominica, West Indies
Fig. 2. Cultured species at the CBP in Dominica. (A) Gryllodes sigillatus. (B) Gryllus assimilis. (C) Caribacusta dominica. (D) Blaberus discoidalis. (E) Zophobas atratus. (F) Veronicella sloanii. (G) Pleurodonte dentiens. (H) Leptogoniulus sp. Photos: D. Nicholson.
Figure 6 in The morphometric and erythrometric analyses of Pelophylax ridibundus living in anthropogenic pollution resources
Figure 6. Other erythrocytic abnormalities: A- IE; immature erythrocyte (arrow), B- ME; mitotic erythrocyte (arrow), C- EE; enucleated erythrocyte (arrow), D- PE; picnotic erythrocyte (arrow), Giemsa.
Figure 4 in The morphometric and erythrometric analyses of Pelophylax ridibundus living in anthropogenic pollution resources
Figure 4. Erythrocytic nuclear abnormalities (2. and 3. stations). A- Bud nucleus (arrow), B- Blebbed nuclei (arrows), C- Kidney shaped nuclei (arrows), D- Binucleated erythrocyte (arrow). Giemsa.
Figure 5 in The morphometric and erythrometric analyses of Pelophylax ridibundus living in anthropogenic pollution resources
Figure 5. Cellular abnormalities of P. ridibundus (3. Station) A- Vacuolized erythrocytes (arrows), B- Erythrocytes with distorted elliptical shape (arrows). Giemsa.
Figure 3 in The morphometric and erythrometric analyses of Pelophylax ridibundus living in anthropogenic pollution resources
Figure 3. The erythrocytes of P. ridibundus. A- Normal erythrocyte (arrow) (1. station), B–D- Erythrocytic nuclear abnormalities (2. and 3. stations); B- Micronucleus (arrow), C- Lobed nucleus (arrow), D- Notched nuclei (arrows). Giemsa.
Figure 2. A in The morphometric and erythrometric analyses of Pelophylax ridibundus living in anthropogenic pollution resources
Figure 2. A- Normal symmetry of the frogs, symmetry line (arrow), (1. station). B- Abnormal symmetry of the frogs, radioulna spot (a), dorsal spots (b), femur spots (c), and tibia spot (d) asymmetries, (2. station). C- Abnormal symmetry of the frogs, femur spot (a), dorsal spots (b), and tarsus spot (c) asymmetries, (3. station). D- Asymmetry in the frog's dorsal midline (arrow) (3. station). SVL: 6,2 cm.
Figure 1. The sampling stations. 1 in The morphometric and erythrometric analyses of Pelophylax ridibundus living in anthropogenic pollution resources
Figure 1. The sampling stations. 1st station (Dereboğazı); Erzurum-Dereboğazı Village, 28.6 km. 2nd Station (Adaçay); Erzurum- Adaçay, 15.7 km. 3rd station (Erzurum State Airport Square); Erzurum-Airport, 12 km (red square; centrum).
Chromosome-level genome assembly of a living fossil, the Atlantic Horseshoe Crab Limulus polyphemus
<p>Associated data for male Atlantic horseshoe crab <em>Limulus polyphemus </em>chromosome-scale genome and annotations, including genome (FASTA), structural gene annotations (GFF3), functional annotations (TSV), coding sequences (CDS), protein sequences (PEP), RepeatModeler library (FA.CLASSIFIED), and repeat annotations (OUT).</p> <p>qaLimPoly3.1 - Publication analyses were completed with this genome. </p> <p>qaLimPoly3.3 - This is the current reference assembly. Assembly updated with Sanger sequencing based edits of Chr11 and removal of adapter contamination. Gene annotations updated with curation of canonical proclotting genes. Repeat annotations updated with curation of repeat elements ltr-1_family-1, ltr-1_family-4, and ltr-1_family-26. </p> <p>HSC_Genomic_FacC_860F_PREMIX_CNNJ42_1.ab1 and HSC_Genomic_FacC_1544R_PREMIX_CNNJ43_2.ab1 are Sanger sequenced PCR products for Lp_g42129 (Factor C) from primers FacC_860F.fasta and FacC_1544R.fasta.</p>
Fig. 2 in Living with liver flukes: Does migration matter?
Fig. 2. Liver fluke prevalence and intensity. Liver fluke prevalence (top; infected animals/all animals sampled) and liver fluke intensity (bottom; EPG) detected in faecal pellets of each elk migrant tactic at the population (left) and individual level (right) separated by sampling year (2017 in dark grey, 2018 in light grey). Bars represent 95% confidence intervals for prevalence and standard error for intensity. Significant differences within years (α = 0.5) are indicated with a,b,c where no letters indicate no significant difference.
Fig. 1 in Living with liver flukes: Does migration matter?
Fig. 1. Study Area Map. The Ya Ha Tinda in relation to Banff National Park in western Canada and locations of elk faecal samples collected in 2017–2018 by migration tactic.
Figure 2. Oiketicus kirby.a. Basket-shaped bag. b in Living inside baskets: a new fruit tree host for Oiketicus kirbyi Guilding, 1927 (Lepidoptera: Psychidae) in Brazil
Figure 2. Oiketicus kirby.a. Basket-shaped bag. b. Dorsal view of larva. c. General view of Jabuticabeira tree. d. Immature Jabuticabeira fruit being eaten by O. kirbyi larva. / Figura 2. Oiketicus kirby. a. Capullo. b. Vista dorsal de la larva de Oiketicus kirbyi. c. Vista general del árbol de Jabuticabeira. d. Fruto inmaduro de Jabuticabeira siendo comido por la larva de O. kirbyi.
Fig. 6 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 6. Stacked frequency distributions of captured Elenchus koebelei males. The white area under the outline illustrates the number of days with a given catch at Wakulla Beach, the gray area depicts that for all years at Guana Tolomato Matanzas National Estuarine Research Reserve (GTM), and the hashed gray area represents the portion of the catch at GTM without 2014. Lastly, the broad outline represents the combined catch frequencies from both sites for all 3 years, 2013–2015. More than half the days with no catches occurred in 2014, when sampling began in mid-Oct.
Fig. 5. Live Elenchus koebelei males caught over a 3 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 5. Live Elenchus koebelei males caught over a 3-year period plotted against minutes relative to sunrise. Most eclosed males were caught between 30 min before sunrise and sunrise itself. None were caught more than 63 min before or 36 min afer sunrise. Though wind-induced fluctuations occurred at Wakulla Beach, the range of capture times at both sites were similar, and peak catch times appear strongly influenced by morning civil twilight. Of the 521 adult male E. koebelei caught over the course of the study, only the 391 captured alive at known times are included in the graph.
Fig. 3 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 3. Collection sites: The north branch of the Guana Tolomato Matanzas National Estuarine Research Reserve in Saint John's County, near Florida's Atlantic Coast, and Wakulla Beach, on the Gulf Coast in Wakulla County. [Produced with assistance from Eco-Regions of Florida. Level IV Ecoregions graphic developed by the Watershed Monitoring Section, Division of Environmental Assessment and Restoration, Florida Department of Environmental Protection, Tallahassee, Florida. Sourced from Griffith et al. (2001). Adapted with permission.]
Fig. 8 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 8. Daily Strepsiptera catch versus temperature and wind speed. Ninetythree percent of the Elenchus koebelei were caught at temperatures between 21.7 to 25.6 °C (71–78 °F) inclusive. Strepsiptera catch suffered markedly when it was too cold. Similarly, most E. koebelei were captured when the wind was blowing slightly, perhaps owing to the role pheromones play. The ×'s indicate conditions in which no Strepsiptera were caught but sampling was attempted. Graphed wind speeds were measured at area weather stations rather than locally.
Fig. 2. The light trap. A in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 2. The light trap. A. Schematic of the PVC skeleton. Electronics were placed in the bucket, which could be suspended from the trap at high tide. B. PVC parts. Some parts were cemented together for strength and ease of construction. C. Trap with sheet and lights in place. In taller grass, longer trap legs can be used to help provide a crease into which attracted Strepsiptera can fly, walk, or fall. This reduces specimen loss through desiccation or drop-off into grass. In short grass it may be better to wet the trap base and use a long ultraviolet light. D. The base of the trap when used with the long light.
Fig. 4 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 4. Successful sampling days, grouped by year and ordered by start time. The figure displays the delay between the beginning of sampling and the first live capture, the time between live captures, and the time afer the last live capture until disbanding of daily sampling. Seven captures were made during astronomical twilight, all of which occurred at Wakulla Beach: 5 on one morning, and 2 on another. There were no sampling days with live catches between 24 and 50 at either site.
Fig. 7 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 7. Influence of initial temperature on total catch. Black boxes indicate the fraction of total Strepsiptera captured at the given temperatures; adjacent hashed boxes represent the fraction of mornings at each temperature. The most productive days were those with dawn temperatures ranging from 22.8 to 25 °C (73–77 °F). Elenchus koebelei was not found to fly on mornings when the temperature was below 17.2 °C (63 °F). The ratio of E. koebelei caught to collection days drops off dramatically for temperatures above 25.5 °C (78 °F).
Fig. 1 in Light trap capture of live Elenchus koebelei (Strepsiptera: Elenchidae)
Fig. 1. Above: Image of an adult male Elenchus koebelei standing on an an- esthetic stage. Note its bifurcated antennae, black tapioca-like eyes, modified forewing that forms a haltere (only 1 of the pair is visible), silver sheen hindwings (iridescent in color images), and extensive thorax. Below: An E. koebelei positioned above a penny for size comparison. [When closing in on a calling female, E. koebelei fly upright with the abdomen tip turned under (Muir 1906).] Adjacent are 3 pictures of visibly stylopized planthoppers. Pupating male E. koebelei bulge from the sides of their hosts. The arrows indicate puparia.
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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.