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605 results for “conservation implication”
FIGURE 1 in Spintherobolus papilliferus in the rio Ribeira de Iguape basin: implications for the biogeography and conservation of an endangered species (Ostariophysi: Characiformes)
FIGURE 1 | Spintherobolus papilliferus sampled in an affluent of rio Juquiá, rio Ribeira de Iguape drainage, municipality of Juquitiba, São Paulo State, Brazil. A. Live specimen right after capture. B. LISO 426, fixed specimen, 33.0 mm SL. Scale bar = 10 mm.
Species diversity and community structure of braconid wasps (Hymenoptera) in two ecological hotspots of Iran: implication for conservation
<p><span><span>Species diversity and community structure of braconid wasps (Hymenoptera) <a name="_Hlk115346465"></a>in two ecological hotspots of <a name="_Hlk115825047"></a><span>Iran</span>: implication for conservation </span></span></p> <p><span>Parisa Abdoli<sup>1</sup>, Ali Asghar Talebi<sup>1</sup></span><a title="" href="#_ftn1" name="_ftnref1"><sup><span><span>*</span></span></sup></a><span>, Nickolas G. Kavallieratos<sup>2</sup>, Samira Farahani<sup>3­</sup> and Rasoul Khosravi<sup>4</sup> </span></p> <p><em><span> </span></em></p> <p><span>1. Department of Entomology, Faculty of Agriculture, Tarbiat Modares University, Tehran, I.R. Iran. <a name="_Hlk533412392"></a>talebia@modares.ac.ir; P.abdoli@modares.ac.ir</span></p> <p><span>2. Laboratory of Agricultural Zoology and Entomology, Department of Crop Science, Agricultural University of Athens; 75 Iera Odos <span> </span>str., 11855 Athens, Attica, Greece. </span><span>nick_kaval@aua.gr</span></p> <p><span>3. Research Institute of Forests and Rangelands, Agricultural Research Education and Extension Organization (AREEO), Tehran, I. R. Iran.<span> </span></span><a href="mailto:s.farahani@rifr-ac.ir"><span>s.farahani@rifr-ac.ir</span></a></p> <p><span><span>4. Department of Natural Resources and Environmental Engineering, College of Agriculture, Shiraz University, Shiraz, Iran, r-khosravi@shirazu.ac.ir</span></span></p> <div><br> <div> <p><a title="" href="#_ftnref1" name="_ftn1"><span><span><span>*</span></span></span></a><span> </span>Correspondence<span>. E-mail: talebia@modares.ac.ir</span></p> <p> </p> </div> </div>
Linked collectors and determiners for: Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation.
Natural history specimen data linked to collectors and determiners held within, "Diversity and distribution of Lentibulariaceae in Bahia state, Brazil: implications for phytogeography and conservation". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/6ea4ec5f-b4df-4321-b36b-557389067003">https://bionomia.net/dataset/6ea4ec5f-b4df-4321-b36b-557389067003</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/6ea4ec5f-b4df-4321-b36b-557389067003">https://gbif.org/dataset/6ea4ec5f-b4df-4321-b36b-557389067003</a>. Formatted as a Frictionless Data package.
Figure 1 in Specialist and generalist species in habitat use: implications for conservation assessment in snakes
Figure 1. Relationship between the diversity scores in habitat use and the number of citations (log transformed) for each snake species in the study area. Each point is one snake species: Ca, Coronella austriaca, Cg, Coronella girondica, Hh, Hemorrhois hippocrepis, Mb, Macroprotodon brevis, Mm, Malpolon monspessulanus, Nn, Natrix natrix, Rh, Rhinechis scalaris, Vl, Vipera latastei.
Figure 2 in Specialist and generalist species in habitat use: implications for conservation assessment in snakes
Figure 2. Principal components plot for different snake species. The percentage of the variance explained by the two main factors is indicated on the axes. Three separate groups of species are indicated. Ca, Coronella austriaca, Cg, Coronella girondica, Hh, Hemorrhois hippocrepis, Mb, Macroprotodon brevis, Mm, Malpolon monspessulanus, Nn, Natrix natrix, Rs, Rhinechis scalaris, Vl, Vipera latastei.
Fig. 2 in Ecological factors that influence sambar (Rusa unicolor) distribution and abundance in western Thailand: implications for tiger conservation
Fig. 2 The distribution of elevations at which transects were placed (a). The distribution of distances from the Huai Kha Khaeng River (HKK) at which transects were placed (b). The combinations of elevation and distance to HKK River at which pellet groups were found (each dot represents a single transect) (c). The number of pellet groups found in relation to distance from the HKK River at three elevations (where dots represents transects) (d). Dots represent transects and lines represent the predicted number of pellet groups using our top-supported model (Table 2, model 1) solved at mean covariate values and one of three elevations to illustrate the interaction of elevation with distance to the HKK River.
Fig.1 in Ecological factors that influence sambar (Rusa unicolor) distribution and abundance in western Thailand: implications for tiger conservation
Fig.1 Location of Huai Khaeng Wildlife Sanctuary in western Thailand and the 360 sampling units contained within the four areas represent six female tiger home ranges.
Fig. 3 in Food preference of the Bornean elephant (Elephas maximus borneensis) in North Kalimantan Province, Indonesia, and its conservation implications
Fig. 3. The OPLS score plot (a) showing the correlation between 1H NMR data and Bornean elephant predictive food preference level. The loading coefficient plot (b) showing the signals that are positively (on the positive y-axis) and negatively (negative y-axis) correlated to the preference prediction [C = Calamus sp., DC = Donax canniformis, EG = Elaeis guineensis, E = Etlingera sp., MB = Musa borneensis, SS = Saccharum spontaneum, BO = Bambusa oldhamii, SO = Saccharum officinarum, CN = Cocos nucifera, AH = Artocarpus heterophyllus, L = Licuala sp., CM = Caryota mitis, AP = Arenga pinanga].
Fig. 2 in Food preference of the Bornean elephant (Elephas maximus borneensis) in North Kalimantan Province, Indonesia, and its conservation implications
Fig. 2. The orthogonal projections to latent structures (OPLS) score plot (a) showing separation of nutritional values among the samples [C = Calamus sp., Dc = Donax canniformis, Eg = Elaeis guineensis, E = Etlingera sp., Mb = Musa borneensis, Ss = Saccharum spontaneum, Bo = Bambusa oldhamii, So = Saccharum officinarum, Cn = Cocos nucifera, Ah = Artocarpus heterophyllus, L = Licuala sp., Cm = Caryota mitis, Ap = Arenga pinanga] The response-related profile (b) showing signals that are positively and negatively correlated to the preference prediction [NDF = Neutral detergent fibre, ADF = Acid detergent fibre, HC = Hemicellulose, ADL = Acid detergent lignin, CP = Crude protein, P = Phosphorus, K = Potassium, Ca = Calcium, Mg = Magnesium, Na = Sodium].
Fig. 1 in Food preference of the Bornean elephant (Elephas maximus borneensis) in North Kalimantan Province, Indonesia, and its conservation implications
Fig. 1. Map of the study area showing transects containing feeding signs of Bornean elephant in the study area in Tulin Onsoi Sub-district, North Kalimantan Province (after Suba et al., 2018).
Fig. 4 in Modelling the change in the distribution of the black-shanked douc, Pygathrix nigripes (Milne-Edwards) in the context of climate change: Implications for conservation
Fig. 4. The predicted distribution of the black-shanked douc (P. nigripes) generated by the MaxEnt software under the RCP8.5 scenario. BGM = Bu Gia Map National Park; CYS = Chu Yang Sin National Park; CT = Cat Tien National Park; HB = Hon Ba Nature Reserve; KL-SM = Kalon-Song Mao Nature Reserve; KT = Krong Trai Nature Reserve; NK = Nam Ka Nature Reserve; NN = Nam Nung Nature Reserve; NC = Nui Chua National Park; NO = Nui Ong Nature Reserve; TK = Takou Nature Reserve; VC = Vinh Cuu Nature Reserve.
Fig. 2 in Modelling the change in the distribution of the black-shanked douc, Pygathrix nigripes (Milne-Edwards) in the context of climate change: Implications for conservation
Fig. 2. The predicted distribution of the black-shanked douc (P. nigripes) generated by the MaxEnt software under the RCP4.5 scenario. BGM = Bu Gia Map National Park; CYS = Chu Yang Sin National Park; CT = Cat Tien National Park; HB = Hon Ba Nature Reserve; KL-SM = Kalon-Song Mao Nature Reserve; KT = Krong Trai Nature Reserve; NK = Nam Ka Nature Reserve; NN = Nam Nung Nature Reserve; NC = Nui Chua National Park; NO = Nui Ong Nature Reserve; TK = Takou Nature Reserve; VC = Vinh Cuu Nature Reserve.
Fig. 3 in Modelling the change in the distribution of the black-shanked douc, Pygathrix nigripes (Milne-Edwards) in the context of climate change: Implications for conservation
Fig. 3. Response curve plots illustrate the dependence of predicted potential distribution on the three most important environmental variables for the black-shanked douc (P. nigripes). The curve shows the mean response of 10 replicates by MaxEnt (red line) and the standard deviation (blue band).
Fig. 1. The 472 in Modelling the change in the distribution of the black-shanked douc, Pygathrix nigripes (Milne-Edwards) in the context of climate change: Implications for conservation
Fig. 1. The 472 points recorded for the black-shanked douc (P. nigripes) that were used in this study. BGM = Bu Gia Map National Park; CYS = Chu Yang Sin National Park; CT = Cat Tien National Park; HB = Hon Ba Nature Reserve; KL-SM = Kalon-Song Mao Nature Reserve; KT = Krong Trai Nature Reserve; NK = Nam Ka Nature Reserve; NN = Nam Nung Nature Reserve; NC = Nui Chua National Park; NO = Nui Ong Nature Reserve; TK = Takou Nature Reserve; VC = Vinh Cuu Nature Reserve.
FIGURE 1 in Variation in the Deterioration of Fossil Resins and Implications for the Conservation of Fossils in Amber
FIGURE 1. Historical deterioration of amber pieces in the AMNH collections: A. Crazing of several old Baltic amber specimens. B. Old Baltic amber piece with insect exhibiting "darkening." C. Same specimen after repolishing. D. "Darkening" of several old Baltic amber specimens. E. Same specimens after repolishing. F. Old Baltic amber piece showing overall deterioration including crazing and large crack through the insect inclusion. G. Same piece after embedding in a high-grade epoxy (EpoTek 301-2).
FIGURE 4 in Variation in the Deterioration of Fossil Resins and Implications for the Conservation of Fossils in Amber
FIGURE 4. Crazing after exposure to a combination of UV/Vis and fluctuating humidity. A. New Jersey sample prior to treatment (size of all samples: 1.5 cm × 1.25 cm × 3 mm). B. New Jersey sample after treatment. C. Detail of crazing on New Jersey sample. D. Burmese sample prior to treatment. E. Burmese sample after treatment. F. Detail of crazing on Burmese sample.
FIGURE 7 in Variation in the Deterioration of Fossil Resins and Implications for the Conservation of Fossils in Amber
FIGURE 7. Images showing effects of heat on amber samples. A. Baltic sample prior to treatment. B. Yellowing of Baltic sample due to heat exposure. C. Burmese sample prior to treatment. D. No discernible yellowing of Burmese sample after heat exposure.
Fig. 1 in Influence of spawning procedure on gametes fertilization success in Salminus hilarii Valenciennes, 1850 (Teleostei: Characidae): Implications for the conservation of this species
Fig. 1. Fertilization rates of Salminus hilarii for G1 (wild broodstock), G2 (domesticated broodstock), G3 (wild females, manually stripped) and G4 (domesticated females, manually stripped) at the Ponte Nova Fish Farm. Values (mean ± standard error of the mean) followed by different symbol are significantly different between experimental groups.
Fig. 2 in Influence of spawning procedure on gametes fertilization success in Salminus hilarii Valenciennes, 1850 (Teleostei: Characidae): Implications for the conservation of this species
Fig. 2. Microscopic aspect of the ovaries and macroscopic aspect of Salminus hilarii larvae: a. micrograph of a mature ovary, showing the vitellogenic oocytes; b. micrograph of the ovary showing an atretic oocyte. Scale bars: (a) 300 m and (b) 100 m;
Fig. 2 in Microsatellite variation and population genetic structure of a neotropical endangered Bryconinae species Brycon insignis Steindachner, 1877: implications for its conservation and sustainable management
Fig. 2. UPGMA clustering of the Nei's genetic distance (1972) of the Brycon insignis sampling locations based on six microsatellite loci. Bootstrap values above 50% are shown above branches indicating percentage support in 5000 permutations. Power Company Hatchery (PCH), São João River (SJR), Paraíba do Sul River (PSR), Imbé River (IMR), Muriaé River (MUR) and Itabapoana River (ITR).
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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.