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552 results for “species abundance”
Figure 6 in Soil Gamasina from savanna and ReviTec site of Ngaoundéré (Adamawa, Cameroon): abundance and species diversity
Figure 6. Mean abundances (ind. in tsd./m2, 0 –10 cm, n = 2) for the three eudominant Gamasina morphospecies (Afrodacarellus spec.1, Multidentorhodacarus cf. aegypticus -a, Afrogamasellus cf. nyinabitabaensis). sav = savanna, others as in Tab. 1.
Figure 5 in Soil Gamasina from savanna and ReviTec site of Ngaoundéré (Adamawa, Cameroon): abundance and species diversity
Figure 5. Mean abundances (ind. in tsd./m2, 0 – 10 cm, n = 2) for the two most dominant Gamasina morphospecies (Rhodacarus cf. matatlanticae, Hypoaspis-Geolaelaps spec.1). sav = savanna, others as in Tab. 1.
Figure 1 in Soil Gamasina from savanna and ReviTec site of Ngaoundéré (Adamawa, Cameroon): abundance and species diversity
Figure 1. Weather data for the Ngaoundéré region, Jan. to Dec. 2016, provided by Ngaoundéré airport meteorological station; 1105 m ASL; precipitation = 1691 mm; temperature mean/min/max = 22/19/25°C; min rel. hum mean/min/max = 45/16/64 %.
Figure 4 in The amount of mulch increases the abundance, and its composition the species diversity of springtails in crop rotation on chernozem soils
Figure 4. Non-metric PCoA plots of the Collembola community The Jaccard similarity coefficient was taken as the distance between dots. (A) plant residues of peas, (B) plant residues of wheat.
Figure 3 in Spatiotemporal distribution, abundance, and species-environment relationships of Scyphozoa (Cnidaria) species in Hisarönü, Marmaris, and Fethiye bays (Muğla, Turkey
Figure 3. RDA ordination plot for Scyphozoa species, environmental parameters, sampling months, and stations. Sampling stations in RDA plot indicated with □: Hisarönü 1; ■: Hisarönü 2; O: Marmaris 1; ●: Marmaris 2; ◇: Marmaris 3; ◆: Marmaris 4; ×: Marmaris 5; ∆: Fethiye 1; △: Fethiye 2; ▲: Fethiye 3. Scyphozoa species indicated by the following abbreviations: Aa: Aurelia aurita; Ct: Cotylorhiza tuberculata; Ca: Cassiopea andromeda. Sampling months in RDA plot indicated with: 1: September 2011; 2: October 2011; 3: November 2011; 4: December 2011; 5: January 2012; 6: February 2012; 7: March 2012; 8: April 2012; 9: May 2012; 10: June 2012; 11: July 2012; 12: August 2012; 13: September 2012; 14: October 2012. See Table 4 for abbreviations of environmental variables.
Fig. 2. Correlations between diversity and abundance across collections. Each record represents a in Streetlights attract a broad array of beetle species
Fig. 2. Correlations between diversity and abundance across collections. Each record represents a night of collection in a given trap. Colors represent traps, with color code being the same as in Figs. 1, 3 and 4. Line represents the regression line between the two variables with intercept forced to 0.
Figure 1 in Mosquito (Diptera: Culicidae) species richness and abundance across a tree-height gradient: does adding CO enhance the BG-Lure?
Figure 1. Study Site and Sampling Setting. (A) Monroe County in Indiana, USA. (B) Hickory Ridge Fire Tower and Nearest Weather Station within Monroe County. (C) BG-pro mosquito trap in CDC style. (D) Tower canopy height gradient. / Figura 1. Sitio de estudio y metodologÍa de muestreo. (A) Condado Monroe, Indiana, Estados Unidos. (B) Torre de avistamiento de incendios y estación meteorológica más cercana dentro del Condado Monroe. (C) Trampa de mosquitos BG-pro configurada en estilo CDC. (D) Gradiente de altitud arbórea.
Pre-exposure of abundant species to disturbance improves resilience in microbial metacommunities. Zenodo fileset.
<p>Data and code for downstream analyses for journal article entitled "Disturbance pre-exposure of abundant species improves community and metacommunity resilience"</p>
Figure 15-16. Rank abundance chart for Phanaeini species. 15 in Diversity and distribution of the scarab beetle tribe Phanaeini in the northern states of the Brazilian Northeast (Coleoptera: Scarabaeidae: Scarabaeinae)
Figure 15-16. Rank abundance chart for Phanaeini species. 15) Recorded in Ceará during February-June 2008. Light grey indicates specimens observed in Atlantic forest; dark grey indicates specimens observed in caatinga. 16) Recorded in Maranhão during February and May 2008. All specimens were broadly observed in cerrado habitat (see species accounts for details).
Figure 2 in Climatic and cultivar effects on phytoseiid species establishment and seasonal abundance on citrus
Figure 2 Abundances (number of individuals per beating sample) of phytoseiid mite species on seedlings in August. A – mean Amblyseius swirskii abundance with and without pollen provisioning. B – The relationship betweenTyphlodromus athiasae andA. swirskii abundances on different cultivars. The order of cultivars appearing in the legend corresponds to the magnitudes of their fitted intercepts (Pomello> Volka> …> Shamouti). Error bars are ± 1 SE
Figure 1 in Climatic and cultivar effects on phytoseiid species establishment and seasonal abundance on citrus
Figure 1 Phytoseiid species abundances (number of individuals per beating sample) on different cul- tivars in April, 5 weeks post release, on seedlings where Euseius stipulatus was released, with pollen provisioning (white bars), on seedlings where Euseius scutalis was released, with pollen provision- ing (gray bars), and on seedlings where no predator was released, without pollen provisioning (black bars). A – Euseius stipulatus abundances. B –Iphiseius degeneransabundances. C –Amblyseius swirskii abundances. Error bars are ± 1 SE.
Figure 3 in Climatic and cultivar effects on phytoseiid species establishment and seasonal abundance on citrus
Figure 3 Mean daily reproductive output per female (panels A and B) and survival rate (of both sexes, panels C and D), ofA. swirskii and E. stipulatus on Pomelo and Shamouti leaf discs in climate-controlled chambers. Panels A and C – Temperature regime 1 (simulating spring temperatures). Panels B and D – Temperature regime 2 (simulating summer temperatures). See Table 2 for the daily temperature schedule of each regime. Note the different scales of reproductive output between the two temperature regimes. Error bars are ± 1 SE.
Figure 13 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 13. Microplana scharffi. The numbers of specimens of each colour category. (a) Using 23 colour categories: figure in parentheses indicates the eight-colour category that the colour is assigned to; (b) using eight colour categories (1–8). Data are ranked from highest to lowest totals.
Figure 11 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 11. Kitchen site: numbers of hatchlings seen each month for 2003 and 2004. (a) Microplana scharffi; (b) Microplana terrestris; (c) khaki Microplana species.
Figure 5 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 5. Microplana scharffi. (a) Monthly occurrence (corrected numbers) over 48 months from March 2001 to February 2005: 1 to 5 on the x-axis are years 2001 to 2005; (b) mean ¡ SE monthly numbers from January (J) to December (D) over 4 years.
Figure 4 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 4. Soil temperature (°C) at the kitchen site. (a) Monthly average from March 2001 to February 2005: 1 to 5 on the x-axis are years 2001 to 2005; (b) mean¡SE values from January (J) to December (D) over 4 years.
Figure 6 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 6. Microplana terrestris. (a) Monthly occurrence (corrected numbers) over 48 months from March 2001 to February 2005: 1 to 5 on the x-axis are years 2001 to 2005; (b) mean¡SE monthly numbers from January (J) to December (D) over 4 years.
Figure 3 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 3. Rainfall (mm). (a) Monthly totals from March 2001 to February 2005: 1 to 5 on the x-axis are years 2001 to 2005; (b) mean¡SE monthly values from January (J) to December (D) over 4 years.
Figure 1 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 1. The kitchen site. (a) General view, with one of the authors (J.M.); (b) close-up of traps.
Figure 12 in Abundance, reproduction, and feeding of three species of British terrestrial planarians: Observations over 4 years
Figure 12. Microplana terrestris. Kitchen site. The mean ¡ SE number of flatworms seen feeding per day per calendar month over 4 years.
ScienceDex guides
Understand access before you commit
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.