Find research datasets worth reusing
Search datasets from major research repositories and use ShareScore to quickly assess how well each record supports discovery, access, and reuse.
1,133
datasets available to search
ShareScore release 0.7.1
Dataset results
1,133 results for “wetlands”
Figure 1 from: Balke M, Ospina-Torres R, Megna YS, Laython M, Hendrich L (2019) A new species of Rhantus diving beetles from the wetlands of the City of Bogota and surroundings (Coleoptera, Dytiscidae, Colymbetinae). Alpine Entomology 3: 169-174. https://doi.org/10.3897/alpento.3.37308
Figure 1 Dorsal habitus of Rhantus andinus (A), R. bogotensis sp. nov. (B), R. vicinus (C), R. franzi (D).
Figure 2 from: Balke M, Ospina-Torres R, Megna YS, Laython M, Hendrich L (2019) A new species of Rhantus diving beetles from the wetlands of the City of Bogota and surroundings (Coleoptera, Dytiscidae, Colymbetinae). Alpine Entomology 3: 169-174. https://doi.org/10.3897/alpento.3.37308
Figure 2 Rhantus spp.: Pronotal margin of R. bogotensis sp. nov. female (A), male (B); R. vicinus female (C); R. bogotensis: surface sculpture on head, frons (D), middle part of pronotum with base and disc (E) elytron, basal area (F).
Supplementary material 2 from: Cohen O, Gamliel A, Katan J, Shubert I, Guy A, Weber G, Riov J (2019) Soil solarization based on natural soil moisture: a practical approach for reducing the seed bank of invasive plants in wetlands. NeoBiota 51: 1-18. https://doi.org/10.3897/neobiota.51.36838
: Data type: measurement
Supplementary material 1 from: Cohen O, Gamliel A, Katan J, Shubert I, Guy A, Weber G, Riov J (2019) Soil solarization based on natural soil moisture: a practical approach for reducing the seed bank of invasive plants in wetlands. NeoBiota 51: 1-18. https://doi.org/10.3897/neobiota.51.36838
: Data type: measurement
Hydrodynamics at Coastal Wetland Edges (HyWEdges)
<p> </p> <p>In this flume experiment, we aimed to quantify the way in which salt marsh and mangrove vegetation edges attenuate incident wave and current energy, modify the nature of the turbulent kinetic energy (TKE), and thus control the sediment transport which determines the rate of progradation or landward retreat. Our results will complement recent work (Maza et al. 2013, Losada et al. 2016, Maza et al. 2013) in order to obtain a better understanding of wave-current flow features at vegetation edges. They will increase our understanding of coastal wetland dynamics, and deliver information that could be used for efforts to increase coastal resilience and therefore protection.</p> <p>References<br>Maza, M., J.L. Lara, and I.J. Losada, A coupled model of submerged vegetation under oscillatory flow using Navier–Stokes equations. Coastal Engineering, 2013. 80: p. 16-34.<br>Losada, I.J., M. Maza, and J.L. Lara, A new formulation for vegetation-induced damping under combined waves and currents. Coastal Engineering, 2016. 107: p. 1-13.<br>Maza, M., J.L. Lara, and I.J. Losada, Solitary wave attenuation by vegetation patches. Advances in Water Resources, 2016. 98: p. 159-172.</p> <p> </p>
Figure 2 in Morphometric and allozymic differences between Bearded Tit Panurus biarmicus (Aves: Passeriformes) subpopulations in a large wetland and a small pond in central Anatolia, Turkey
Figure 2. Comparison of average wing length and average tail length of the different Bearded Tit populations.
Figure 2 in Nest characteristics and breeding success of Sarus Crane, Antigone antigone (Linnaeus, 1758) (Aves: Gruidae) in different habitats at Dhanauri Wetland, Uttar Pradesh, India
Figure 2. Study area in Gautum Budh Nagar district, Noida, Uttar Pradesh showing roads (black lines) to monitor Sarus Crane nests and their breeding success during the study period, location of villages in red circles with names, wetlands> 40 ha (blue polygon) and village ponds> 8 ha (dark gray polygon). In the top left, the insets show the location of Uttar Pradesh in India (with state boundaries) and the blue spot in Uttar Pradesh blue spot shows Gautum Budh Nagar District.
Figure 1. A in Interesting rotifers (Rotifera: Eurotatoria) from a subtropical wetland of Meghalaya, Northeast India: new records
Figure 1. A) Map of India showing Meghalaya state; B) District map of Meghalaya showing Shillong (East Khasi hills district). Table. Variations in some basic abiotic parameters.
Figures 2–9. 2 in Interesting rotifers (Rotifera: Eurotatoria) from a subtropical wetland of Meghalaya, Northeast India: new records
Figures 2–9. 2- Colurella tesselata (Glascott) (lateral view); 3- Lecane stichaea Harring (ventral view); 4- Gastropus minor (Rousselet) (lateral view); 5- Stephanoceros fimbriatus (Goldfusz) (lateral view); 6- Dissotrocha aculeata (Ehrenberg) (lateral view); 7- Lecane dorysimilis Trinh Dang, Segers & Sanoamuang (dorsal view); 8- Cupelopagis vorax (Leidy) (lateral view); 9- Cupelopagis vorax (Leidy) (trophi).
Figure 3 in Structural characteristics of the soil fauna community in beach wetlands of the Poyang Lake region
Figure 3. Distribution of soil fauna in the 0–20 cm soil layer at different sampling sites in the Poyang Lake region.
Figure 2 in Structural characteristics of the soil fauna community in beach wetlands of the Poyang Lake region
Figure 2. Numbers of soil fauna individuals and groups at different sampling sites in Poyang Lake wetlands.
Figure 5 in Spatiotemporal patterns of ground beetle diversity (Coleoptera: Carabidae) in a Ramsar wetland (Chott Tinsilt) of Algeria
Figure 5. Hierarchical clustering dendrogram illustrating abundance-based similarity of ground beetle species among months in Chott Tinsilt, northeastern Algeria (clustering method = Euclidean paired group, UPGMA).
Figure 3 in Diurnal time-activity budget and foraging techniques of red-crested pochards (Netta rufina) wintering at the wetlands of West Bengal, India
Figure 3. Month-wise and time-wise proportional time budget of the RCPs. Values are given in percentages of the time spent in the diurnal activities (mean value ± SD; n = 32; 96-h observation).
Figure 1 in Diet of the Lesser Spotted Eagle (Clanga pomarina) in Amvrakikos Wetlands National Park, Greece
Figure 1. Aerial photo of Valaoritis mountain with Quercus frainneto forest in foreground, where a nesting territory of lesser spotted eagle was active in 2000 (Photo: S. Zogaris).
Fig. 2 in Investigating the role of urbanisation, wetlands and climatic conditions in nematode parasitism in a large Australian elapid snake
Fig. 2. Abundance (mean number nematodes per snake) of stomach nematodes in adult SW WA tiger snakes based on specimen collection time period. Bars represent standard errors and dots represent outliers, n = sample size for each period.
Diversity, Species Richness and Community Composition of Wetland Birds in the Lowlands of Western Nepal
Open the record for dataset details and reuse information.
FIGURE 8 in Prionohydrus cambyreta sp. nov. from Iberá wetlands-the first species of the genus from northern Argentina (Coleoptera: Noteridae)
FIGURE 8. Known distributional data for the species of Prionohydrus.
Table 4 in Temperate grassy wetlands of South Africa: Description, classification and explanatory environmental factors
<p><b>Table 4</b> Description of vegetation types of temperate grassy wetlands.</p><table><tbody><tr><th>No.</th><th>Wetland vegetation type</th><th>No. comm.</th><th>Dominant species</th><th>Vegetation structure</th><th>Environmental conditions</th><th>Distribution</th><th>Comments</th><th>Species diversity</th></tr></tbody><tbody><tr><th>1</th><td>Waterbiesie</td><td>2</td><td><i>Eleocharis dregeana, Leersia</i></td><td>Dense, medium tall sedges or</td><td>Mostly pans, gleyed clay soils,</td><td>Inland parts of Eastern South</td><td><i>Leersia hexandra</i> is the most common</td><td>Median 6</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>dregeana</i></td><td>grasses (20–50 cm tall)</td><td>seasonally or permanently wet</td><td>Africa</td><td>wetland grass in South Africa</td><td>(1–23)</td></tr><tr><th>2</th><td>Pond sedge wetlands</td><td>1</td><td><i>Carex acutiformis</i></td><td>Dense medium tall sedges (30–80</td><td>Mostly valley bottom wetlands, on</td><td>Inland parts of Eastern South</td><td>The species <i>Carex acutiformis</i> is</td><td>Median 4</td></tr><tr><th></th><td></td><td></td><td></td><td>cm tall)</td><td>clay or peat, permanently wet</td><td>Africa, mostly around the</td><td>widely distributed and it is not clear</td><td>(1–18)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>escarpment</td><td>whether it is indigenous to South</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Africa</td><td></td></tr><tr><th>3</th><td>Grassy everlasting</td><td>1</td><td><i>Aristida junciformis,</i></td><td>Dense short grassland (20–50 cm tall)</td><td>Seasonally or temporarily wet</td><td>Inland parts of Eastern South</td><td>Conspicuous because of the presence</td><td>Median 13</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Helichrysum aureonitens</i></td><td></td><td>grasslands, mostly on loam soils</td><td>Africa, most common around the</td><td>of the everlasting <i>Helichrysum</i></td><td>(5–24)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Drakensberg</td><td><i>aureonitens</i></td><td></td></tr><tr><th>4</th><td>Highveld mixed</td><td>6</td><td><i>Cyperus denudatus,</i></td><td>Dense medium tall to tall sedge or</td><td>Various habitats, mostly in valley</td><td>Widespread in Eastern South</td><td>Few communities are dominated by</td><td>Median 8</td></tr><tr><th></th><td>sedge wetlands</td><td></td><td><i>Schoenoplectus brachyceras,</i></td><td>grassland (20–120 cm tall)</td><td>bottom wetlands and floodplains, on</td><td>Africa, but also in the Cape</td><td>grasses, but the wetter communities</td><td>(1–22)</td></tr><tr><th></th><td></td><td></td><td><i>Juncus effusus</i></td><td></td><td>clay or loam soils of different wetness</td><td></td><td>by sedges and rushes</td><td></td></tr><tr><th>5</th><td>Eragrostis</td><td>1</td><td><i>Eragrostis planiculmis</i></td><td>Dense tall grassland (80–120 cm)</td><td>Temporarily to seasonally wet clay soils</td><td>Inland parts of Eastern South</td><td></td><td>Median 9</td></tr><tr><th></th><td>planiculmis wetlands</td><td></td><td></td><td></td><td></td><td>Africa</td><td></td><td>(3–19)</td></tr><tr><th>6</th><td>Chichi mixed</td><td>2</td><td><i>Arundinella nepalensis,</i></td><td>Dense tall grassland (80–120 cm) or</td><td>Temporarily to seasonally wet loam</td><td>Inland parts of Eastern South</td><td>The bush ‘Chichi’ or ‘Ouhout’ becomes</td><td>Median 11</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Leucosidea sericea</i></td><td>short grassland with shrubs up to 3 m.</td><td>soils, mostly in mountainous terrain</td><td>Africa, most common around the</td><td>dominant in disturbed grasslands, but</td><td>(3–24)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Drakensberg</td><td>also in floodplains and seepages</td><td></td></tr><tr><th>7</th><td>Rooivleigrass</td><td>3</td><td><i>Hemarthria altissima,</i></td><td>Open to dense, medium tall grassland</td><td>Mostly around the edge of pans or</td><td>Inland parts of eastern South</td><td></td><td>Median 9</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Cyperus marginatus,</i></td><td>or sedgeland (30–60 cm)</td><td>valley bottom wetlands, on temporarily</td><td>Africa, extending into the Western</td><td></td><td>(2–34)</td></tr><tr><th></th><td></td><td></td><td><i>Paspalum dilatatum</i></td><td></td><td>to seasonally wet loam soils</td><td>Free State</td><td></td><td></td></tr><tr><th>8</th><td>Red grass wetlands</td><td>1</td><td><i>Themeda triandra</i></td><td>Dense short grassland (20–50 cm tall)</td><td>Temporarily wet grassland areas</td><td>Widespread across the Highveld</td><td>The grass <i>Themeda triandra</i></td><td>Median 11</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>and around the Drakensberg</td><td>represents the most dominant grass</td><td>(3–26)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>species in the upland areas of the</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>Highveld region, and it can deal</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>reasonably well with inundation</td><td></td></tr><tr><th>9</th><td>Cyperus fastigiatus</td><td>1</td><td><i>Cyperus fastigiatus</i></td><td>Dense tall sedgeland (100–180 cm</td><td>Permanently wet areas in valley bottom</td><td>Throughout the country, including</td><td>Different forms of the species occur,</td><td>Median 6</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td>tall)</td><td>wetlands, either on clay or peat</td><td>the Cape and tropical areas, but</td><td>especially in the tropical areas</td><td>(1–16)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>absent from the drier areas</td><td></td><td></td></tr><tr><th>10</th><td>Silver spike grass</td><td>4</td><td><i>Imperata cylindrica,</i></td><td>Medium tall to tall mixed</td><td>Temporarily to seasonally wet,</td><td>Mostly in the Northern Highveld,</td><td><i>Imperata cylindrica</i> is commonly</td><td>Median 10</td></tr><tr><th></th><td>wetlands</td><td></td><td><i>Miscanthus junceus</i></td><td>grasslands (50–120 cm)</td><td>mostly sandy areas</td><td>Northern KwaZulu-Natal and in the</td><td>found in disturbed soils, for example</td><td>(2–30)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td>Cape</td><td>in road verges</td><td></td></tr><tr><th>11</th><td>Eragrostis plana</td><td>1</td><td><i>Eragrostis plana</i></td><td>Open to dense medium tall</td><td>Temporarily or seasonally wet loam</td><td>Inland parts of Eastern South Africa</td><td>Often an indicator of disturbance</td><td>Median 11</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td>grassland</td><td>or clay soils</td><td>as well as the Cape</td><td></td><td>(4–27)</td></tr><tr><th>12</th><td>Common bullrush</td><td>1</td><td><i>Typha capensis</i></td><td>Dense tall reedlands</td><td>Seasonally to permanently wet clay or</td><td>Common in Northern South Africa,</td><td>The dominant species occurs often in</td><td>Median 4.5</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td></td><td>peat soils, often with high nutrient</td><td>Natal and the Cape</td><td>urban wetlands as it can deal very</td><td>(1–18)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>loads</td><td></td><td>well with pollution and high nutrient</td><td></td></tr><tr><th></th><td></td><td></td><td></td><td></td><td></td><td></td><td>loads</td><td></td></tr><tr><th>13</th><td>Common reed</td><td>1</td><td><i>Phragmites australis</i></td><td>Open to dense tall reedlands</td><td>Many different habitats, mostly</td><td>Throughout the whole country</td><td>One of the most competitive wetland</td><td>Median 4</td></tr><tr><th></th><td>wetlands</td><td></td><td></td><td></td><td>seasonally to permanently wet, also</td><td></td><td>plants. Benefits from high nutrient</td><td>(1–30)</td></tr><tr><th></th><td></td><td></td><td></td><td></td><td>dealing well with salinity</td><td></td><td>loads and stabilized water levels.</td><td></td></tr></tbody></table>
Data from: Aggregation but not organo-metal complexes contributed to C storage in tidal freshwater wetland soils
One of the many goals of wetland restoration is to promote the long-term storage of carbon (C) in the terrestrial biosphere. Unfortunately, soil C reservoirs in restored wetlands are slow to accumulate even after hydrology and plant communities are reestablished. Oftentimes wetland restoration changes the soil matrix and thus can dramatically alter how soil C is stored and processed. Our research investigated whether soil organic matter (SOM) preservation theories derived from studies in non-wetland soil systems can be extended to wetland soils. We examined C associated with water-stable soil aggregates, minerals, and metal oxides within habitats of one natural and one restored tidal freshwater wetland. This study revealed that a majority of the soil C in the natural site was associated with large macroaggregates (> 2000 μm), and soils from the restored site stored more C in small macroaggregates (> 250 to < 2000 μm). Despite these different associations, the chemical composition of SOM followed similar patterns across each aggregate-size class. Results from the sequential extraction procedure suggest organo-metal oxide complexes do not contribute to C stabilization in these habitats. This research is one of the few studies that have examined C stabilization related to soil structure in wetland soils. Our results suggest soil aggregate formation may be an important mechanism driving C stabilization, and that disruption to macroaggregates may limit C accumulation in restored wetlands. Additional empirical research and long-term field monitoring are needed to confirm linkages between aggregate-C stabilization and accumulation in wetland soils.
Figure 1 in Diversity of aquatic bird species in a wetland complex in southern Chile
Figure 1. Study area, Lanalhue Lake, Biobío Region, Chile.
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.