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184 results for “freshwater habitat”
Figure 5 in Predatory insects in lentic freshwater habitats from northwest Patagonia: richness and phenology
Figure 5. Phenology of predatory insects (black bar = adult stage; white bar = coleopteran larva; single-hatched bar = odonate nymph; double-hatched bar = hemipteran nymph), and climate data (precipitation = black circles; minimum temperatures = white triangles; maximum temperatures = black triangles) from June 2006 to March 2007.
Figure 4 in Predatory insects in lentic freshwater habitats from northwest Patagonia: richness and phenology
Figure 4. Monthly variation in predatory insect richness in the wetlands studied, showing mean richness (± SE) for the wetlands classified according to their hydroperiod.
Figure 3 in Predatory insects in lentic freshwater habitats from northwest Patagonia: richness and phenology
Figure 3. Comparison of the richness of predatory insects in three types of wetlands, classified according to the duration of the hydroperiod. Different letters indicate significant differences in species richness (P <0.01).
Figure 2 in Predatory insects in lentic freshwater habitats from northwest Patagonia: richness and phenology
Figure 2. Predatory insect distribution in the study area. Distribution index was obtained by the ratio: number of wetlands with species i/total number of wetlands sampled.
Figure 1 in Predatory insects in lentic freshwater habitats from northwest Patagonia: richness and phenology
Figure 1. Map of the study area surrounding the city of San Carlos de Bariloche. Numbers refer to wetland location: 1 = Llao-Llao; 2 = Laguna El Trébol; 3 = Mallín 2 de Agosto; 4 = Laguna Fantasma; 5 = Virgen de las Nieves; 6 = Mallín Pinar de Festa; 7 = Teleférico; 8 = Mallín Ñireco, Ñireco 1 and Ñireco 2; 9 = Laguna Verde; 10 = Mallín Los Patos; 11 = Bernal 1–6; 12 = Ñirihuau 1–4. The triangle indicates the location of the meteorological station.
Figure 3 in Renewed sampling of inland aquatic habitats in southern Africa yields two novel freshwater crab species (Decapoda: Potamonautidae: Potamonautes)
Figure 3. Potamonautes bellarussus sp. nov., female from the Mecula mountains in the Niassa province, Mozambique, showing the bright-red colour of the freshwater crab while alive.
Figure 4 in Renewed sampling of inland aquatic habitats in southern Africa yields two novel freshwater crab species (Decapoda: Potamonautidae: Potamonautes)
Figure 4. Potamonautes bellarussus sp. nov., male holotype (carapace length = 39.29 mm) from the Yao Mountains, 1045 m a.s.l., 12°27′276″ S, 36°32′260″ E, Niassa province, Mozambique (SAM A 48212): A, whole animal, dorsal aspect; B, whole animal, ventral aspect; C, cephalothorax, frontal aspect. Scale bars: 10 mm.
Figure 8 in Renewed sampling of inland aquatic habitats in southern Africa yields two novel freshwater crab species (Decapoda: Potamonautidae: Potamonautes)
Figure 8. Potamonautes flavusjo sp. nov., male holotype, Verloren Vallei Nature Reserve (site B), Mpumalanga province of South Africa (SAM A 48203). A, left gonopod 1, anterior view; B, left gonopod 1, posterior view; C, left gonopod 2, anterior view. Scale bars: 10 mm.
Figure 7 in Renewed sampling of inland aquatic habitats in southern Africa yields two novel freshwater crab species (Decapoda: Potamonautidae: Potamonautes)
Figure 7. Potamonautes flavusjo sp. nov., male holotype (carapace length = 24.02 mm) Verloren Vallei Nature Reserve (site B), 2000 m a.s.l., 25°20′333 ″ S, 30°07 ′546 ″ E, Mpumalanga province of South Africa (SAM A 48203): A, whole animal, dorsal aspect; B, whole animal, ventral aspect; C, cephalothorax, frontal aspect. Scale bars: 10 mm. The right cheliped was broken off prior to capture.
Figure 5 in Renewed sampling of inland aquatic habitats in southern Africa yields two novel freshwater crab species (Decapoda: Potamonautidae: Potamonautes)
Figure 5. Potamonautes bellarussus sp. nov., male holotype from the Yao Mountains, Niassa province, Mozambique (SAM A 48212): A, left gonopod 1, anterior view; B, left gonopod 1 posterior view; C, left gonopod 2 anteri- or view. Scale bars: 10 mm.
FIGURE2 in Aquatisphaeria thailandica gen. et sp. nov. (Tetraplosphaeriaceae, Pleosporales) from freshwater habitat in Thailand
FIGURE2. Aquatisphaeria thailandica (MFLU 20-0687, holotype) a–c. Colonies on woody subtrate. d–i. Conidia attached to conidiophores. j. Conidiogenous cell. k–n. Conidia. o. Upper view of the colony on PDA. p. Reverse view of the colony on PDA. Scale bars: d–i = 30 μm, j–n = 10 μm.
FIGURE 1 in Aquatisphaeria thailandica gen. et sp. nov. (Tetraplosphaeriaceae, Pleosporales) from freshwater habitat in Thailand
FIGURE 1. Phylogenetic tree generated from maximum likelihood (ML) analysis based on combined LSU, ITS and SSU sequence data. ML bootstrap support values greater than 75% and Bayesian posterior probabilities (PP) greater than 0.95 are given above the nodes, branches with 100% ML BP and 1.0 PP are in thickened. Taxa representing by type speciments (or ex-type strains) are highlighted in bold. Newly generated sequences are indicated in red. The tree is rooted with Amniculicola immersa (CBS 123083) and A. parva (CBS 123092). The figures on the right side show the morphology of the type species in each genus.
FIGURE 1 in Xylochrysis aquatica sp. nov. (Woswasiaceae) from freshwater habitats in Sichuan Province, China
FIGURE 1. Phylogenetic tree generated from ML analyses of a combined ITS, LSU, SSU, tef1-α and rpb2 dataset. Bootstrap support values for ML ≥ 75% are placed above the branches and Bayesian posterior probabilities (BYPP) ≥ 0.95 are shown as bold branches. Ex-type strains are in bold and new strains generated in this study are indicated in red. The tree was rooted to Pleurostoma repens (CBS 294.39).
FIGURE 2 in Xylochrysis aquatica sp. nov. (Woswasiaceae) from freshwater habitats in Sichuan Province, China
FIGURE 2. Xylochrysis aquatica (HKAS 124019, holotype) a, b Appearance of ascomata on the host surface. c Vertical section of ascomata. d Ostiole. e Vertical section through ascomatal wall. f Hamathecium. g Apical ring stained with Lugol's iodine reagent. h–l Asci. m–o Ascospores. p Germinating ascospore. q Colony from above. r Colony from below. Scale bars: c, d = 50 μm, e, f, h–l = 20 μm, p = 10 μm, g, m–o = 5 μm.
FIGURE 4 in Parafuscosporella lignicola sp. nov. (Fuscosporellaceae), from a freshwater habitat in northern Thailand
FIGURE 4. Sporulation of Parafuscosporella lignicola (XXX ex-type) on PDA. a Germinated conidium on PDA. b Obverse (left) and reverse (right) views of a colony on PDA. c–g Hyphae, conidiophores, conidia and conidiogenous cells from culture. Scale bars: a, c = 20 μm, d = 50 μm, e–g =20μm.
FIGURE 1 in Parafuscosporella lignicola sp. nov. (Fuscosporellaceae), from a freshwater habitat in northern Thailand
FIGURE 1. Phylogenetic tree constructed from RAxML analysis of a combined ITS, LSU and SSU, sequence data. Bootstrap support values for ML equal or greater than 75% and Bayesian posterior probabilities greater than 0.95 PP are indicated at the nodes. The ex-type strains are in bold, and the new isolates are in red bold.
FIGURE 3 in Parafuscosporella lignicola sp. nov. (Fuscosporellaceae), from a freshwater habitat in northern Thailand
FIGURE 3. Parafuscosporella lignicola (MFLU22-0101 holotype). a Specimen b, c Colonies on substrate. d, e Conidiophores with conidia. f–i Conidiogenous cells and conidia. j Conidia. Scale bars: d = 10μm, e = 20μm, f–j = 10 μm.
FIGURE 2 in Parafuscosporella lignicola sp. nov. (Fuscosporellaceae), from a freshwater habitat in northern Thailand
FIGURE 2. The results of the pairwise homoplasy index (PHI) test for Parafuscosporella lignicola and closely related species using LogDet transformation. PHI test results (Φw) <0.05 indicate significant recombination within the dataset.
Prediction of current and future suitable habitats for three invasive freshwater fish species (Lepomis gibbosus, Perccottus glenii and Pseudorasbora parva) in Europe
<p><span>Climate change can have a significant impact on the earth's ecosystems. Invasive species will respond to climate change, and their responses will have ecological and economic implications. Habitat suitability models (HSMs) are one of the most important tools currently available to assess the potential impacts of climate change on species. Projections of models of suitable conditions for species, built using Maxent based on the occurrence throughout the range (native and invasive), on the current climate of Europe and on the forecast climate data for the 2050s and 2070s under the SSP2 and SSP5 scenarios are present here.</span></p>
FIGURE 2 in Triplosphaeria guizhouensis sp. nov. (Tetraplosphaeriaceae, Pleosporales), a novel taxon from freshwater habitat in Guizhou Province, China
FIGURE 2. Triplosphaeria guizhouensis (GZAAS20-0407, holotype). a, b Colonies on natural substrate. c–f Conidia bearing 3–4 appendages. g Germinating conidium. h, i Culture on PDA, h from above, i from below. Scale bars: c–f=25 μm. g =50 μm.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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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.