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Figure 3 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 3 Stations in which Graphoderusbilineatus was captured in the Motte reserve in 2014 (green) and in 2018 (yellow). The dotted lines represent the reserve boundaries and the grey points the sampled stations (2018) in which no Graphoderusbilineatus were captured. Background picture obtained from the Swiss Federal Office of Topography swisstopo.
Figure 1 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 1 Graphoderusbilineatus. Copyright: Yerpo [CC BY-SA 4.0 (https://creativecommons.org/licenses/by-sa/4.0)], from Wikimedia Commons.
Figure 5 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 5 Principal component (PC) for habitat depth, helophyte cover and hydrophyte cover for G.bilineatus (green) and G.cinereus (blue). The first principal component (PC1) explains 59% of the variance. The first two components (PC1 and PC2) explain 81% of the total variance. While factor loads of habitat depth, helophyte cover and hydrophyte cover for PC1 are similar, helophyte cover and depth strongly negatively influence PC2. Circles represent 95% probability ellipses.
Figure 2 from: Knoblauch A, Gander A (2019) Distribution of a residual population of the Dytiscid Graphoderus bilineatus (de Geer, 1774) in the Grande Cariçaie nature reserves, Switzerland. Alpine Entomology 3: 83-91. https://doi.org/10.3897/alpento.3.30417
Figure 2 Location of the sampling stations in the Grande Cariçaie nature reserves, on the south eastern shore of Lake Neuchâtel. We sampled seven reserves in 2018 (delimited in brown polygons): 1) Grèves de Cheseaux, 2) Baie d'Yvonand, 3) Cheyres, 4) Grèves de la Corbière et de Chevroux, 5) Grèves d'Ostende et de Chevroux, 6) Grèves de la Motte and 7) Cudrefin. The orange points represent the sampled stations (N = 101 stations). Background picture obtained from the Swiss Federal Office of Topography swisstopo.
Propellant and Gunshot Residue Profiles Obtained With GunShotMatch
<p>This dataset contains the following profiles:</p> <ul> <li>Gunshot residue from Sellier & Bellot 9 mm Parabellum FMJ, Batch 4211/9</li> <li>Gunshot residue from Sellier & Bellot 9 mm Parabellum, Batch 843 (old stock)</li> <li>Gunshot residue from Magtech 9 mm Parabellum LRN, Batch BA0916 L-93</li> <li>Gunshot residue from Magtech Cleanrange 9 mm Parabellum JSP, Batch BA0910 L-01</li> <li>Gunshot residue from CBC 9 mm Parabellum FMJ, Batch AQD518 L-430 (old stock)</li> <li>Propellant and gunshot residue from Eley Contact .22 Long Rifle</li> <li>Propellant and gunshot residue from Geco Rifle .22 Long Rifle</li> <li>Propellant and gunshot residue from Winchester Pistol .22 Long Rifle (old stock)</li> <li>Alliant Unique reloading propellant</li> </ul> <p> </p> <p>These profiles were obtained with GunShotMatch (https://doi.org/10.5281/zenodo.2669156) following Gas Chromatography-Mass Spectrometry</p> <p> </p>
Functionally Important Residues from Graph Analysis of Co-evolved Dynamical Couplings
<p>This dataset contains input files and trajectories for class A β-lactamase SHV-1.</p>
FIG. 2 in First Systematic Study using the Variability of the Residual Colour Patterns: The Case of the Paleogene Seraphsidae (Mollusca, Gastropoda, Stromboidea)
FIG. 2. — Variability of the extant species Terebellum terebellum (Linnaeus, 1758) in dorsal view and normal light: A-D, T. terebellum form punctulorum (RÖding, 1798); E, T. terebellum form delicatum Kuroda & Kawamoto, 1961, MNHN IM, Segond Channel, Santo, Vanuatu; F-J, T. terebellum form nebulosum (RÖding, 1798); A, MNHN IM, Grand Récif Sud, New Caledonia; B, MNHN IM, Grand Récif Sud, New Caledonia; C, MNHN IM, Secteur de Balabio, New Caledonia; D, MNHN IM, Grand Récif Sud, New Caledonia; F, MNHN IM, Plateau des Chesterfield; G, MNHN IM, Plateau des Chesterfield); H, MNHN IM, Aésé Island, Santo, Vanuatu; I, MNHN IM, Baie des Citrons, Nouméa, New Caledonia; J, MNHN IM, Quatre Bancs de l'Ouest, lagoon of Nouméa, New Caledonia; K, T. terebellum, MNHN IM, Plateau des Chesterfield. Scale bars: 10 mm. Photographs by C. Lemzaouda (MNHN).
Paraquat residues in soya products intended for animal feed (monitoring results from 2018-2019)
<p>Monitoring results for paraquat residues in soya products intended for animal feed. 174 samples were analyzed in 2018 and 2019.</p>
Figure 8 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 8 - a–d Colour images of abundant species: a Quedius labradorensis Smetana b Gabrius brevipennis (Horn) c Pseudopsis subulata Herman d Pterostichus punctatissimus (Randall).
Figure 7 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 7 - a–d Colour images of abundant species: a Atheta capsularis Klimaszewski b Atheta klagesi Bernhauer c Atheta strigosula Casey d Tachinus fumipennis (Say).
Figure 5 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 5 - Boxplots depicting catch rates (beetles/day) for eight abundant species collected from experimental plots where forest was a clearcut and deadwood was left intact (SOH) b clearcut with quantity of deadwood reduced (WTH), and c uncut forest (Control). Bold line depicts median value, box denotes 25–75% quantile range, whiskers correspond to 1.5 times the interquartile range.
Figure 6 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 6 - Multivariate regression tree based on sum-of-squares depicting differences in beetle assemblages among experimental plots where forest was a clearcut with stem-only harvested (SOH) b clearcut with whole-tree harvested (WTH), and c uncut forest (Control). The tree was selected based on 935/1000 cross-validations and explains 64% of the variance. Both experimental treatment and deadwood volumes provided equivalent improvement at each split. We have labelled splits using experimental treatments.
Figure 4 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 4 - Boxplots depicting overall catch rates (beetles/day) where forest was a clearcut and deadwood was left intact (SOH) b clearcut with quantity of deadwood reduced (WTH), and c uncut forest (Control). Bold line depicts median value, box denotes 25–75% quantile range, whiskers correspond to 1.5 times the interquartile range.
Figure 3 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 3 - Boxplots showing volume of fine and coarse woody debris in stem-only harvested plots (SOH), whole-tree harvested plots (WTH), and in uncut forest (Control). Bold line depicts median value, box denotes 25–75% quantile range, whiskers correspond to 1.5 times the interquartile range.
Figure 1 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 1 - Schematic representation of treatments with pitfall trap locations, Forêt Montmorency, Quebec.
Figure 2 from: Klimaszewski J, Work T, Thiffault E, Bourdon C, Pare D, Bousquet Y, Venier L, Titus B (2013) Initial responses of rove and ground beetles (Coleoptera, Staphylinidae, Carabidae) to removal of logging residues following clearcut harvesting in the boreal forest of Quebec, Canada. ZooKeys 258: 31-52. https://doi.org/10.3897/zookeys.258.4174
Figure 2 - Photographs of experimental plots taken one year following harvest (2012) A, B photos of uncut forests (Control) C stem-only harvested plot (SOH) (operational level) D whole-tree harvested plot (WTH).
Procyanidins from cranberry press residues - extraction opti-mization, purification and characterization HRMS data
<p>Data of HRMS</p>
Pesticide residue monitoring in South Tyrol (Italy)
<ul> <li>Pesticide residue monitoring programm in South Tyrol (Province Bolzano, Italy)</li> <li>The programm is organized and conducted by the Department of Public Health, Servizio Igiene e Sanità<br> Pubblica—Azienda Sanitaria dell’Alto Adige, Bolzano, Italy</li> <li>Further despription and data available at: <ul> <li>https://www.sabes.it/gesundheitsvorsorge/umweltmedizin.asp</li> <li>https://umwelt.provinz.bz.it/pestizide-suedtirol.asp</li> </ul> </li> <li>Residue concentrations of grass samples per sampling site and sampling date can be found in the file "Pesticide_monitoring_SouthTyrol_2018_2021.csv "</li> <li>Available period: 2018 to 2021</li> <li>All sampling sites were public sites</li> <li>Names of active agents are in Italian</li> <li>Residue concentartions are given in "mg kg<sup>-1</sup>"</li> <li>"n.d." means "not detected"</li> <li>Lower limit of quantification (LOQ) was by default 0.01 mg kg<sup>-1</sup></li> <li>GPS coordinates of the sampling sites are can be found in thefile "Coordinates_sampling_sites.csv"</li> </ul>
Data for: Combined effects of GBH residues and phosphate fertilizers on endophytic microbiota and plant performance of garden strawberry
<p>Aims: In a field study, the effects of treatments of glyphosate-based herbicides (GBHs) in soil, alone and in combination with phosphate fertilizer, were examined on the performance and endophytic microbiota of garden strawberry. </p> <p>Methods and results: The root and leaf endophytic microbiota of garden strawberries grown in GBH-treated and untreated soil, with and without phosphate fertilizer were analyzed. Next, bioinformatics analysis on the type of 5-enolpyruvylshikimate-3-phosphate synthase enzyme was conducted to assess the potential sensitivity of strawberry-associated bacteria and fungi to glyphosate, and to compare the results with field observations. GBH treatments altered the abundance and/or frequency of several operational taxonomic units (OTUs), especially those of root-associated fungi and bacteria. These changes were partly related to their sensitivity to glyphosate. Still, GBH treatments did not shape the overall community structure of strawberry microbiota or affect plant performance. Phosphate fertilizer increased the abundance of both glyphosate-resistant and glyphosate-sensitive bacterial OTUs, regardless of the GBH treatments.</p> <p>Conclusions: These findings demonstrate that although the overall community structure of strawberry endophytic microbes is not affected by GBH use, some individual taxa are.</p> <p>Significance and impact of study: Agrochemical residues in soil can shape the endophytic microbiota in crop plants.</p>
Influence of grain size, organic carbon and organic matter residue content on the sorption of per-and polyfluoroalkyl substances in aqueous film forming foam contaminated soils-Implications for remediation using soil washing
<p>Supporting information from Influence of grain size, organic carbon and organic matter residue content on the sorption of per-and polyfluoroalkyl substances in aqueous film forming foam contaminated soils-Implications for remediation using soil washing</p>
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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.