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1,154 results for “Pooling”

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dryad28/100

Subsampling and DNA pooling can increase gains through genomic selection in switchgrass

<p>Genomic selection (GS) can accelerate breeding cycles in perennial crops such as the bioenergy grass switchgrass (<i>Panicum virgatum</i> L.). The sequencing costs of GS can be reduced by pooling DNA samples in the training population (TP), only sequencing TP phenotypic outliers, or pooling candidate population (CP) samples. These strategies were simulated for two traits (spring vigor and anthesis date) in three breeding populations. Sequencing only the outlier 50% of the TP phenotype distribution resulted in a penalty of &lt;5% of the predictive ability, measured using cross-validation. Predictive ability also decreased when sequencing progressively fewer TP DNA pools, but TPs constructed from only two phenotypically contrasting DNA samples retained a mean of &gt;80% predictive ability relative to individual TP sequencing. Novel group testing methods allowed greater than one CP individual to be screened per sequenced DNA sample but resulted in a predictive ability penalty. To determine the impact of reduced sequencing, genetic gain was calculated for seven GS scenarios with variable sequencing budgets. Reduced TP sequencing and most CP pooling methods were superior to individual sequence-based GS when sequencing resources were restricted (2,000 DNA samples per 5-yr cycle). Only one scenario was superior to individual sequencing when sequencing budgets were large (8,000 DNA samples per 5-yr cycle). This study highlights multiple routes for reduced sequencing costs in GS.</p>

opencc-zeroFeb 2022View details →
dryad28/100

Taxonomic and functional diversity covary in rock pool microalgal communities despite their different drivers - Environmental and diatom data

<p>We sampled 30 brackish‐watered, isolated rock pools once a month (17 May, 22 June, and 22 July) in 2016 on a granitic outcrop in the western island of Pihlajasaari (66°68′449″N, 38°40′48″E), ca. 2 km south of Helsinki, Finland on the coast of the northern Baltic Sea. We examined the drivers and covariance of taxonomic and functional diversity among the rock pool communities. We measured water pH, conductivity, and temperature in the field, and pool morphometrics (i.e., max depth, length, and width) to the nearest centimeter, and calculated pool area (length * width). We collected a 0.5 L water sample from each pool for the determination of total P (SFS‐EN ISO 2004). We estimated pool X and Y coordinates (based on the perpendicular pool distance from the shore and the horizontal pool distance from the map origin in the southern end parallel to the shoreline, respectively) and mean isolation as a mean Euclidean distance (i.e., the sum of distances to five closest pools divided by five; Vanschoenwinkel et al. 2007) for each pool from a drawn grid map of the study area showing the relative location of the sampled pools to each other and to the seashore.</p> <p>We sampled benthic diatoms by collecting epilithic samples (ca. 25 cm<sup>2</sup>) from each pool bottom with a toothbrush, following EN 13946 standard (2003). A total of 500 valves per sample were counted and identified to the lowest taxonomic level possible (mostly species level) with a light microscope. We created a taxonomic site‐species matrix based on species relative abundances.</p> <p>The identified diatom species were classified into 21 partly overlapping functional groups. We first divided the species into five size classes after their biovolume (determined by cell length, width, thickness, and shape) and 14 life‐form categories after interspecific morphological adaptations to physical and chemical disturbance (i.e., cell motility, posture, and type of adhesion) following Rimet &amp; Bouchez (2012). A single taxon may have various successive life forms and may thus be classified into multiple life‐form categories. We further classified the species after their preferences for nutrient concentration and physical disturbance into four ecological guilds (high profile, low profile, motile and planktonic) after Passy (2007) and Rimet &amp; Bouchez (2012). Finally, we separated between acid‐tolerant (acidobiontic or acidophilus species with pH optimum &lt;7 in Van Dam et al. (1994), and nitrogen‐fixing species (with cyanobacterial endosymbionts capable of fixing atmospheric nitrogen). In the species‐trait matrix, each species belonging to a given guild (other than continuous biovolume guild on a scale 1–5) was given a value of 1; otherwise, the value was set to 0. Each species could be characterized by multiple traits and could thus belong to more than only one guild.</p>

opencc-zeroJul 2022View details →
zenodo28/100

Supplementary material 1 from: Niehues A, de Visser C, Hagenbeek FA, Karu N, Kindt ASD, Kulkarni P, Pool R, Boomsma DI, van Dongen J, van Gool AJ, `t Hoen PAC (2022) A Multi-omics Data Analysis Workflow Packaged as a FAIR Digital Object. Research Ideas and Outcomes 8: e94042. https://doi.org/10.3897/rio.8.e94042

Members of the ACTION Consortium

opencc-zeroAug 2022View details →
zenodo28/100

Supplementary material 1 from: DeWalt RE, South EJ (2015) Ephemeroptera, Plecoptera, and Trichoptera on Isle Royale National Park, USA, compared to mainland species pool and size distribution. ZooKeys 532: 137-158. https://doi.org/10.3897/zookeys.532.6478

Table S1. Raw specimen data in the form of an Excel comma delimited file:

opencc-by-4.0Nov 2015View details →
zenodo28/100

Figure 2 from: Kwun H, Park J, Kim H, Kim J, Park H (2017) Checklist of the tidal pool fishes of Jeju Island, Korea. ZooKeys 709: 135-154. https://doi.org/10.3897/zookeys.709.14711

Figure 2 - A Hyporhamphus sajori, MFD-746, 77.3 mm standard length (SL) B Sebastes inermis, MFD-902, 47.5 mm SL.

opencc-by-4.0Oct 2017View details →
zenodo28/100

Figure 10 from: Kwun H, Park J, Kim H, Kim J, Park H (2017) Checklist of the tidal pool fishes of Jeju Island, Korea. ZooKeys 709: 135-154. https://doi.org/10.3897/zookeys.709.14711

Figure 10 - A Lepadichthys frenatus, MFD-318, 47.5 mm SL B Luciogobius guttatus, MFD-144, 50.2 mm SL.

opencc-by-4.0Oct 2017View details →
zenodo28/100

Figure 4 from: Kwun H, Park J, Kim H, Kim J, Park H (2017) Checklist of the tidal pool fishes of Jeju Island, Korea. ZooKeys 709: 135-154. https://doi.org/10.3897/zookeys.709.14711

Figure 4 - A Pseublennius percoides, MFD-671, 47.8 mm SL B Pseudoblennius marmoratus, MFD-927, 19.3 mm SL.

opencc-by-4.0Oct 2017View details →
zenodo28/100

Figure 6 from: Kwun H, Park J, Kim H, Kim J, Park H (2017) Checklist of the tidal pool fishes of Jeju Island, Korea. ZooKeys 709: 135-154. https://doi.org/10.3897/zookeys.709.14711

Figure 6 - A Plesiops coeruleolineatus, MFD-860, 82.8 mm SL B Lutjanus fulviflamma, MFD-866, 101.1 mm SL.

opencc-by-4.0Oct 2017View details →
zenodo28/100

Figure 9 from: Kwun H, Park J, Kim H, Kim J, Park H (2017) Checklist of the tidal pool fishes of Jeju Island, Korea. ZooKeys 709: 135-154. https://doi.org/10.3897/zookeys.709.14711

Figure 9 - A Stethojulis interrupta terina, MFD-850, 92.9 mm SL B Stethojulis trilineata, MFD-482, 25.7 mm SL.

opencc-by-4.0Oct 2017View details →
zenodo28/100

Fig. 11 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 11. Conceptual model of the distribution patterns of eggs and larvae in the early stages of two environments in the Peixe River (upper Uruguay River), from October 2011 to March 2012.

opencc-by-4.0Sep 2014View details →
zenodo28/100

Fig. 6 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 6. Average density ± standard deviation of the macrozooplankton organisms captured in both environments (rapids and pool) of the Peixe River, between October 2011 and March 2012.

opencc-by-4.0Sep 2014View details →
zenodo28/100

Fig. 4 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 4. Average repletion degree (%) of the captured larvae digestive tract from both environments of the Peixe River, from October 2011 to March 2012. Number of larvae examined is shown in brackets. Repletion degree: E - empty; PE - partially empty; PF - partially full; F - full.

opencc-by-4.0Sep 2014View details →
zenodo28/100

Fig. 8 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 8. Average density ± standard error of the larvae captured in the Peixe River with light traps in different environments and months from October 2011 to March 2012.

opencc-by-4.0Sep 2014View details →
zenodo28/100

Fig. 5 in Pools and rapids as spawning and nursery areas for fish in a river stretch without floodplains

Fig. 5. Average flow and precipitation ratings registered in the Peixe River, from October 2011 to March 2012. Source: Consórcio de Itá.

opencc-by-4.0Sep 2014View details →
zenodo28/100

Fig. 5 in New record of four ciliates (Protozoa, Ciliophora) collected from rocky intertidal pools of South Korea

Fig. 5. Photomicrographs of Dysteria semilunaris from living specimens (A-D) and protargol impregnated specimens (E, F). A. Left lateral view of typical individual. B. longitudinal groove on left plate (arrowheads). C. Ventral view. D. Right lateral view showing the two contractile vacuoles (arrows) and the longitudinal groove on the right plate (arrowheads). E, F. Left views of stained specimens showing infraciliature, arrow denotes the short row below the end of the frontoventral kineties. Co, circumoral kineties; CVP, contractile vacuole pore; Cy, cytopharynx; EF, equatorial fragment; FVK, frontoventral kineties; LF, left frontal kineties; LK, left kineties; Ma, macronucleus; P, podite; Pr, preoral kinety; RK, right kineties; TF, terminal fragment. Scale bars: 20 μm.

opencc-by-4.0Dec 2020View details →
zenodo28/100

Fig. 2 in New record of four ciliates (Protozoa, Ciliophora) collected from rocky intertidal pools of South Korea

Fig. 2. Photomicrographs of Aspidisca polypoda from living specimens (A-D), protargol impregnated specimens (E, F), and illustrations (G-J). A. Ventral view showing posterior part of the adoral membranelles (arrowhead). B. Eight distinctive ridges (arrowheads) and contractile vacuole (arrow). C. Anterior part of the adoral membranelles (arrowhead). D. Separated into two parts of leftmost transverse cirri (arrowhead). E, F. Ventral and dorsal view of stained specimens. G-J. Illustrations showing main characteristics. AZM 1 and 2, adoral zone of membranelles 1 and 2; CV, contractile vacuole; DK, dorsal kineties; FVC, frontoventral cirri; MA, macronucleus; TC, transverse cirri. Scale bars: 20 μm.

opencc-by-4.0Dec 2020View details →
zenodo28/100

Cold pool collisions

<p>This dataset contains data used in a publication regarding cold pool collisions.</p>

opencc-by-4.0Nov 2018View details →
zenodo28/100

Figure 9 from: Ando K (2019) The study of amphipods in rimstone pools of Akiyoshi-do Cave, Japan. Subterranean Biology 32: 81-94. https://doi.org/10.3897/subtbiol.32.35031

Figure 9 Result of CCA analysis on the amphipod abundances and water characteristics. TN: total nitrogen, TP: total phosphorus, TB: total number of bacteria, TVB: total number of viable bacteria. Other symbols mean pools surveyed in each season by "month-pool number": for example, 5-CH1 corresponds to CH1 pool surveyed in May.

opencc-by-4.0Nov 2019View details →
zenodo28/100

Figure 5 from: Ando K (2019) The study of amphipods in rimstone pools of Akiyoshi-do Cave, Japan. Subterranean Biology 32: 81-94. https://doi.org/10.3897/subtbiol.32.35031

Figure 5 Pools with arrows pointing the flowing directions. Water from the walls and drips was supplied to CH4 and water flowed to CH2 and CH1 via CH5. Pumped cave river water was supplied to CH8 and CH9 and water flowed to CH6 and CH7.

opencc-by-4.0Nov 2019View details →
zenodo28/100

Figure 8 from: Ando K (2019) The study of amphipods in rimstone pools of Akiyoshi-do Cave, Japan. Subterranean Biology 32: 81-94. https://doi.org/10.3897/subtbiol.32.35031

Figure 8 Fluctuation of the population density of Gammarus nipponensis in the type C pools (1971–1975, 2015–2016).

opencc-by-4.0Nov 2019View 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