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.
566
datasets available to search
ShareScore release 0.7.1
Dataset results
566 results for “pond”
Figure 1 in Environmental niche modelling of the Chinese pond mussel invasion in Europe under climate change scenarios
Figure 1. Map of records of S. woodiana in Europe obtained from GBIF database and published sources (Vikhrev et al., 2024).
Figure 3 in Water quality assessment in an irrigation pond based on adult caddisfly (Insecta: Trichoptera) assemblages
Figure 3. Canonical Correspondence Analysis (CCA) showing correlation between caddisflies species and physicochemical variables. Abbreviations for taxonomy are shown in Table 2.
Figure 2 in Water quality assessment in an irrigation pond based on adult caddisfly (Insecta: Trichoptera) assemblages
Figure 2. The total number of species and individuals caught at an irrigation pond in the Kasetsart University, Thailand.
Figs. 9-14. 9. Lorong Banir, pond 2 in Aquatic Coleoptera Of Singapore: Species Richness, Ecology And Conservation #
Figs. 9-14. 9. Lorong Banir, pond 2. Fully covered with dense stands of the submerged freshwater macrophyte Hydrilla verticullata. Habitat of Canthydrus morsbachi, Laccophilus siamensis siamensis, Hydaticus bipunctatus conjungens, Allocotocerus muelleri, Amphiops mater sumatrensis, Enochrus esuriens, Helochares taprobanicus, H. lentus, H. pallens and Coelostoma subditum; 10. Central Catchment Area, Edge of Nee Soon Swamp Forest: The mats of floating grasses are the habitat of three Neohydrocoptus and eight Singaporean Hydrovatus species; 11. Central Catchment Area, Nee Soon Swamp Forest near former pumphouse. Hydaticus fabricii, Hydrovatus sinister, H. stridulus, H. pudicus, Amphiops mater sumatrensis, Helochares lentus and Enochrus gaggermeieri occur in this pond; 12. Central Catchment Area, temporary puddle on forest floor. Habitat of Copelatus oblitus and C. minutissimus;13. Bukit Timah Nature Reserve. Taban Valley, open forest stream. The shaded springlet of this stream, a true relic site, is the habitat for the most restricted and endangered water beetles in Singapore. Microdytes elgae, M. pasiricus, Lacconectus krikkeni and two species of the genus Hydranea; 14. Central Catchment Area. Shaded, slow flowing and oxygen rich artificial stream in second growth forest. Habitat of most species of the whirligig genus Orectochilus.
Figure 2 in First molecularly substantiated records of the pond snail Ampullaceana fontinalis in the Siverskyi Donets River Basin, Ukraine (Gastropoda: Lymnaeidae)
Figure 2. Voucher of PS43 specimen, Ampullaceana fontinalis, from the Borova River, Luhansk region, Ukraine.
Figure 3 in First molecularly substantiated records of the pond snail Ampullaceana fontinalis in the Siverskyi Donets River Basin, Ukraine (Gastropoda: Lymnaeidae)
Figure 3. Phylogenetic relationships within the genus Ampullaceana obtained using the maximum likelihood optimality criterion based on COI sequences (Log-likelihood of the tree = -4245.7847). Values of both the SH-like approximate likelihood-ratio test (SH-aLRT) and ultrafast bootstrapping are shown for branches.
Fig. 1. A–C in The first case of Spiroxys contortus in European pond turtle (Emys orbicularis) in the wild in Poland
Fig. 1. A–C Female of Spiroxys contortus (Gnathostomatidae) parasite of wild Emys orbicularis (European pond turtle) in Poland. A. Anterior region (a) median lobe with a tooth; (b) the lip with submedian papilla; (c) cuticular spine on the margin of the collar; B. Posterior region with a conical tip (arrow) C. Vulvar opening (arrow).
Fig. 2 in Black-spotted pond frog Pelophylax nigromaculatus as a new host for the renal coccidian genus Hyaloklossia (Alveolata: Apicomplexa)
Fig. 2. Phylogenetic tree of based on cox1 sequences of Hyaloklossia and related species belonging to Toxoplasmatinae (Toxoplasma, Neospora, Hammondia, Heydornia), Cystososporinae (Cystoisospora) and Eumonosporinae (Eumonospora) constructed using the neighbor joining method. The nodes are labeled using support from the bootstrap values obtained for the neighbor joining (left) and maximum likelihood (right) methods. Pn: Pelophylax nigromaculatus.
Fig. 1 in Black-spotted pond frog Pelophylax nigromaculatus as a new host for the renal coccidian genus Hyaloklossia (Alveolata: Apicomplexa)
Fig. 1. Light microscopy of Hyaloklossia oocysts in the kidney of Pelophylax nigromaculatus. A. Immature oocyst showing the sporont with granular cytoplasm that does not fill the space inside the oocyst completely. B. An immature oocyst showing the sporoblast with very thin wall. C. An immature oocyst (left) and mature sporocyst (right). D. A mature oocyst with two sporocysts. Arrowhead and arrows indicate oocyst wall and sporocyst residuum, respectively. Scale bar = 5 μm.
Fig. 3 in Fatal spirorchiidosis in European pond turtles (Emys orbicularis) in Switzerland
Fig. 3. Phylogenetic analysis, (a) Maximum likelihood phylogenetic tree of 206 bp of the 28S rRNA gene of members of the family Spirorchiidae, with Alaria alata as outgroup. Members of the Spirorchis genus are boxed. Parasite names are provided, followed by host names (top clade only), GenBank accession numbers and country of parasite discovery. Bootstrap values above 70 are shown, and branch lengths corresponding to the number of base substitutions are indicated by the scale bar. (b) Unrooted phylogenetic network of 274 bp of the ITS2 region of Spirorchis spp. recently described from North Amercian turtle species (Roberts et al., 2019) and Swiss Emys orbicularis. Host names, location of discovery and GenBank accession numbers are given. Note that the unnamed Spirorchis parasite described from Graptemys ernsti (AL, United States) is 100% identical in both the partial 28S rRNA (MH843487), and ITS2 (MH678746) sequences amplified from all Swiss turtle specimens.
Fig. 2 in Fatal spirorchiidosis in European pond turtles (Emys orbicularis) in Switzerland
Fig. 2. Histopathological findings, (a) Five-year-old female European pond turtle (Emys orbicularis, ID2), small intestine. Multiple intravascular trematode eggs (narrow arrowheads) are present in the tunica muscularis, and submucosa associated with severe granulomatous inflammation and acute haemorrhage (large arrowheads). H&E staining, bar 500 μm. (b) Eleven-year-old female European pond turtle (Emys orbicularis, ID4), large intestine. The mucosa displays a focal deep ulceration (arrows) with replacement of the underlying submucosa and tunica muscularis by fibrous tissue (stars) and severe granulomatous coelomitis (asterisks). Multiple trematode eggs are present intravascularly, particularly in the subserosal vasculature (arrowheads). H&E staining, bar 200 μm. (c) ID2, small intestine. Focal granulomatous reaction with multinucleated giant cells (arrows) displaying intracytoplasmic, partially disrupted trematode eggs (arrowheads). H&E staining, bar 100 μm. (d) Adult male European pond turtle (Emys orbicularis ID5), testis. Interstitial granulomatous reaction composed of multinucleated giant cells (arrows) displaying intracytoplasmic embryonated (arrowheads) and non-embryonated (asterisk) trematode eggs. H&E staining, bar 50 μm.
Fig. 1 in Fatal spirorchiidosis in European pond turtles (Emys orbicularis) in Switzerland
Fig. 1. Gross findings and parasitology, (a) Gastrointestinal tract from a 6-year-old female European pond turtle (Emys orbicularis, ID8) displaying large numbers of spirorchiid eggs in the subserosal vessels (arrowheads), which are more visible in the intestine. Note the focal stricture of the intestine (arrow) with proximal severe dilation. This section was filled with a large amount of necrotic material. Bar 1 cm. (b) Autolytic testis from ID5 displaying similar lesions to the ones observed in the gastrointestinal tract from ID8 (arrowheads). Bar 25 mm. (c) Aspect of a spirorchiid egg stained with methylene blue identified following sedimentation from intestinal content. Light optical microscope, Bar 10 μm. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Data on spatiotemporal thermokarst pond characteristics from a permafrost peatland, northern Sweden
<p>Data related to the article: <span><span>Seemann</span><span>, </span><span>F.</span></span><span> & </span><span><span>Sannel</span><span>, </span><span>A.B.K.</span></span><span> (</span><span>2024</span><span>) </span><span>Morphology and dynamics of thermokarst ponds in a subarctic permafrost peatland, northern Sweden</span><span>. </span><span>Earth Surf. Process. Landforms</span><span>, Available from: </span><a href="https://doi.org/10.1002/esp.6021" target="_blank" rel="noopener">https://doi.org/10.1002/esp.6021</a><span>.</span></p> <p>Each file contains metadata information. Detailed information on data aquisition can be found in the article. </p> <p>Study area: Dávvavuopmi, northern Sweden (68°28'N, 20°54'E)</p> <p>Fieldwork was conducted 24 August – 3 September 2021.</p> <p> </p> <p> </p> <p> </p>
Environmental Factors of Mount Saint Helens Ponds During Summer 2022
<p>This repository contains data collected in summer 2022 about environmental factors in 20 ponds near Mount Saint Helens, as well as code for characterizing the quality of thermal refuges in these ponds.</p>
PASS Survey - Brasside Pond, Durham
<p>Acoustic Survey at Brasside Pond Durham. Recorded using a Sony M10 and Aquarian Audio H2a in accordance to the PASS protocol. </p>
Sea ice, snow and melt pond example data from MOSAiC transect observations
<p>This data set contains in-situ observation of sea ice, snow and melt pond properties from two days in winter (January 23, 2020) and summer (July 7, 2020) during the Multidisciplinary drifting Observatory for the Study of Arctic Climate (MOSAiC) expedition. It originates from two sensors:</p> <ol> <li>Broad-band electromagnetic induction sensor (Geophex GEM-2) measuring the combined thickness of the sea ice and snow layers</li> <li>A GPS snow depth probe (Snow-Hydro MagnaProbe) measuring the thickness of the snow layer and melt ponds depth during summer</li> </ol> <p>Both sensors were operated coincidently along transect loops while different loops were used in both days. This data set is a subset of similar weekly activities between October 2019 and September 2020. This publication intends to provide a preview of the data properties and approximate changes between the winter and summer periods. It also has to be noted, that the final data of the EM induction sensor might differ from this release, which is based on a quick-look processing directly after data acquisition.</p> <p><em>GEM-2 data files</em></p> <p>The file format of GEM-2 data is a text file with comma-separated values. Notable parameters are:</p> <ul> <li>‘time’: UTC time</li> <li>‘longitude’: Longitude in degrees east (fill value: 0.0)</li> <li>‘latitude’: Latitude in degrees north (fill value: 0.0)</li> <li>‘`f{frequency}Hz_hcp_{i:Inphase|q:Quadrature}`: total (ice + snow) thickness of the sea ice and snow layers in meter for different channels*</li> </ul> <p>*The channels correspond to the real (Inphase) or imaginary (Quadrature) part of the EM signal at a given frequency. The variable name in the csv file is to be read as `f{frequency}Hz_hcp_{i:Inphase|q:Quadrature}`. It is recommended to use the Inphase component of the 18.325 kHz frequency (variable `f18325Hz_hcp_i`) for analysis.</p> <p><em>MagnaProbe data files</em></p> <p>The file format of MagnaProbe data is a text file with comma-separated values. Notable parameters are:</p> <ul> <li>`timestamp`: Timestamp</li> <li>`longitude_a`: longitude degree in degrees east</li> <li>`longitude_b`: longitude minute</li> <li>`latitude_a`: latitude degree in degrees north</li> <li>`latitude_b`: latitude minute</li> <li>`depthCm`: Snow thickness or melt ponds depth in cm</li> <li>`flag`: flag value indicating the type or measurement*</li> </ul> <p>Flag values are:</p> <ul> <li>-1 : melt pond</li> <li>1 : snow or surface scattering layer depth,</li> <li>2 : mixed surface type when pond water pools at the base of a melting</li> </ul> <p>The filenames follow the naming convention of <sensor>-mosaic-transect-<date>-<device-operations-id>.csv with the device operation id as a unique identifier of the sensor raw data within the MOSAiC project.</p>
Figure 2 in Terrestrial and communal nesting in Eupemphix nattereri (Anura, Leiuperidae): interactions with predators and pond structure
Figure 2. Several aspects of the predation of Eupemphix nattereri by the whistling heron (Syrigna sibilatrix). Above: a couple of herons, each one with an adult E. nattereri in the beak. Middle: a male heron with an amplectant pair of E. nattereri in his beak (the male frog did not release the female and both escaped predation). Below: a female heron washing an adult E. nattereri prior to consumption; note the foam released by the frog while being washed. Note also in the above and middle pictures, the communal foam nests at the pond's margin. More illustrations on several aspects of the natural history of the species are at the Amphibiaweb (http://elib.cs.berkeley.edu).
Figure 1 in Terrestrial and communal nesting in Eupemphix nattereri (Anura, Leiuperidae): interactions with predators and pond structure
Figure 1. Above: foam nest anchoring in Eupemphix nattereri. Note that the foam nest (, 40 h old) is on a platform excavated in the soil and far from the water level (thin arrow). There are also platforms (thick arrow) to the left that are unoccupied. Bar,9 cm. Below: a nearly 40-h-old collapsing foam nest. Note the wet mucous string through which the early tadpoles moved towards the water. Scale bar, 6 cm.
Figure 3 in Factors influencing spatial and temporal structure of frog assemblages at ponds in southeastern Brazil
Figure 3. Distribution of nine tadpole species within ponds at Santuário do Caraça, southeastern Brazil, according to variables used to describe microhabitats used by them and period of occurrence, in the first three axes of discriminant space. In the first discriminant axis, smaller values represent larger association to the bottom. In the second axis, the largest values indicate use of deeper microhabitats by tadpoles. In the third axis, larger values indicate species that used both microhabitats with and without aquatic vegetation, and lower values indicate species that used only microhabitats with aquatic vegetation. Centroids for each species are shown on the right.
Figure 1 in Factors influencing spatial and temporal structure of frog assemblages at ponds in southeastern Brazil
Figure 1. Mean monthly temperatures and monthly rainfall at the study site between September 2003 and December 2004.
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.