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706 results for “protected area.”
FIGURE 17 in A new species of Gomphoides Selys, 1854 (Odonata: Gomphidae) from the Environmental Protection Area of the Uberaba River, Brazil
FIGURE 17. Distribution of the hitherto known species of Gomphoides in South America, based on minimal convex polygons using sites of occurrence.
FIGURE 10–16 in A new species of Gomphoides Selys, 1854 (Odonata: Gomphidae) from the Environmental Protection Area of the Uberaba River, Brazil
FIGURE 10–16. Gomphoides infumata, male from REGUA, Rio de Janeiro, Brazil (10), cerci and epiproct in lateral view (11) (© Tom Kompier); G. perdita, male from Uberlândia, Minas Gerais, Brazil (12), cerci and epiproct in lateral view (13) (© Diogo Vilela); G. praevia, male holotype, habitus in dorsal view (14), cerci and epiproct in lateral (15) and dorsal (16) views (© NHMW NoaS Image Collection / Harald Bruckner).
Distribution. WC Laos, from S Bolikhamsal Province, probably with the Nam Kading River as the N barrier of the distribution, S to C Khammouane Province, at ¢.17° 40' N; there are also reports from the corridor to Nakai-Nam-Theun National Protected Area, and from Khamkeut District, close to Lak Sao (18° 13' N, 104° 47' E). in Cercopithecidae
Distribution. WC Laos, from S Bolikhamsal Province, probably with the Nam Kading River as the N barrier of the distribution, S to C Khammouane Province, at ¢.17° 40' N; there are also reports from the corridor to Nakai-Nam-Theun National Protected Area, and from Khamkeut District, close to Lak Sao (18° 13' N, 104° 47' E).
Data from: Sundaic elephants prefer habitats on the periphery of protected areas
<p><span>1. </span><span>Protected Areas (PAs) are a cornerstone of global conservation strategies. PAs, however, are not equally effective for all threatened taxa, and it is important to understand taxa-specific effectiveness of PAs networks. </span></p> <p><span>2. </span><span>In this study we evaluate the role of the PAs network on the protection of Asian elephants (<em>Elephas maximus</em>) and their habitats in Southeast Asia's Sundaic region. Since Asian elephants tend to prefer secondary forests or forest gaps, </span><span>we predicted that PAs would not represent the species' preferred habitats.</span> <span>We conducted the most comprehensive analysis of Asian elephant space and habitat use to date through home range estimations and Step Selection Function analyses using over 600,000 GPS locations from 102 different elephants from Peninsular Malaysia and Borneo. </span></p> <p><span>3. </span><span>Our results revealed important similarities in the habitat use of elephants in both regions, with both females and males in Peninsular Malaysia and Sabah preferring secondary forest, forest gaps, and areas of regrowth and new plantations. </span></p> <p><span>4. </span><span>Our results supported our prediction that PAs do not represent Asian elephants' preferred habitats, since for most of the elephants, more than half of their ranges were outside PAs and the probability of selection values for both sexes in both geographical areas were lower inside than outside the PAs. </span></p> <p><span>5. </span><span>Synthesis and applications:</span><span> Our analysis suggests that conservation strategies need to acknowledge that the long-term survival of Asian elephants in the Sundaic region relies on our capacity to promote human-elephant coexistence at the boundaries of PAs. We advocate that Asian elephant conservation strategies should be based on the following three key points: 1) large PAs with core areas where elephants can find safety and potentially survive in the long term; 2) promoting connectivity among PAs using a system of wildlife corridors; and 3) effective human-elephant conflict management outside PAs. </span></p>
Figs 1–8 in A new Andrena species (Hymenoptera: Andrenidae) from the overlooked Doñana Protected Areas of southern Spain
Figs 1–8. Andrena ramosa sp. nov. female. 1, habitus in lateral view. 2, face. 3, clypeus detail. 4, scutum. 5, episternum, viewed from behind. 6, propodeal corbicula. 7, flocculus. 8, terga.
Figs 9–16 in A new Andrena species (Hymenoptera: Andrenidae) from the overlooked Doñana Protected Areas of southern Spain
Figs 9–16. Process of the labrum of Andrena ramosa sp. nov. and Andrena (L.) females. 9, A. ramosa sp. nov. 10, A. tunetana Schmiedeknecht, 1900. 11, A. leptopyga Pérez, 1895. 12, A. barbilabris (Kirby, 1802).13, A. sericata Imhoff, 1868. 14, A. argentata Smith, 1844. 15, A. parviceps Kriechbaumer, 1873. 16, A. ventralis Imhoff, 1832.
Environmental Justice, Marine Protected Areas, & Ocean Access in California -- Ocean_Justice
<p>Coastal California is home to a network of Marine Protected Areas (MPAs) that aim to safeguard the state's marine resources and ecosystems. Little is known about who is served and not served by California's MPAs, with large gaps in environmental justice implications. Our study aimed to investigate access to MPAs across communities in California using multiple lines of evidence, with a focus on subsistence fishers (pier fishers and others who do not sell their catch) who are often indirectly marginalized by MPAs. To address this, we 1) conducted a literature review on equity and environmental justice (EEJ) in California's ocean management policies, 2) compared time traveled to MPAs for zip codes of different demographics, 3) conducted a literature review on subsistence fishing in California, and 4) compared demographics of subsistence fishers with intensity of ocean-based pollution linked to fished species. Our EEJ literature review highlighted a gap in policies addressing equitable ocean access. Our spatial analysis revealed disparities in coastal access by age, race, and income. Our subsistence fishing literature review highlighted that little is known about California's current subsistence fishing, though biophysical aspects are better studied than socioeconomic aspects. Our analysis of pollution and subsistence fishing suggested that many subsistence fishers from disadvantaged communities are fishing in areas with high pollution. State and federal agencies can utilize our results to develop effective future management strategies for equitable access to California's MPAs that take disadvantaged communities into account, especially subsistence fishers, to increase their representation in the decision-making process.</p>
Outputs from fitted models across the cross-validation scenarios for 'Space-time species distribution modeling with opportunistic presence-only data: a case study of passerines in a protected area'
<p>Three Zenodo repositories are linked to the preprint <em>Space-time Species Distribution Modeling for Opportunistic Presence-Only Data: A Case Study of Passerines in a Protected Area </em>(Lasgorceux et al., unpublished, <a href="https://hal.science/hal-04616332">https://hal.science/hal-04616332</a>):</p> <ul> <li>Data, scripts and, code (Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12545052">https://doi.org/10.5281/zenodo.12545052</a>)</li> <li>Outputs from fitted models across the cross-validation scenarios (Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12544212">https://doi.org/10.5281/zenodo.12544212</a>)</li> <li>Supplementary information at (Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12541412">https://doi.org/10.5281/zenodo.12541412</a>)</li> </ul> <p>This repository contains the outputs from fitted models across the cross-validation scenarios.</p> <p>In the folder <em>Ouputs_cross_validation</em>, each species is represented by a .RData file, numbered from 1 to 77 (excluding 7, which corresponds to <em>Bombycilla garrulus</em>; see the preprint for details). This dataset is specifically used to generate Figure 1, which shows the AUC of various cross-validation scenarios. To reproduce this figure in R, place all the files in the <em>Results/Fitted_models</em> folder and run the <em>Models_Outputs.R</em> script located in the <em>Results</em> folder of Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12545052">https://doi.org/10.5281/zenodo.12545052.</a></p> <p>Note: These data have been separated due to memory requirements (23.14GB).</p>
Data, scripts and code for 'Space-time species distribution modeling with opportunistic presence-only data: a case study of passerines in a protected area'
<p>Three Zenodo repositories are linked to the preprint <em>Space-time Species Distribution Modeling for Opportunistic Presence-Only Data: A Case Study of Passerines in a Protected Area </em>(Lasgorceux et al., unpublished, <a href="https://hal.science/hal-04616332">https://hal.science/hal-04616332</a>):</p> <ul> <li>Data, scripts, and code (Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12545052">https://doi.org/10.5281/zenodo.12545052</a>)</li> <li>Outputs from fitted models across the cross-validation scenarios (Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12544212">https://doi.org/10.5281/zenodo.12544212</a>)</li> <li>Supplementary information at (Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12541412">https://doi.org/10.5281/zenodo.12541412</a>)</li> </ul> <p>This repository contains data, scripts, and code. It is organized into two main directories: <em>Materials and Methods,</em> and <em>Results</em>.</p> <h2>Materials and Methods</h2> <p>The raw data can be accessed in the <em>Materials_and_Methods/Data directory</em>. The processed data used for modeling is available in <em>Materials_and_Methods/Data_for_modeling/Data_for_modeling.RData</em>. All scripts for data processing are located in <em>Materials_and_Methods/Processing_scripts</em>. The <em>Plots_and_Figures </em>directory<em> </em>includes illustrations of the data used for modeling, such as PCA correlation plots presented in Supplementary information. The main script for running the model for each species is <em>Main_script.R</em>.</p> <h2>Results</h2> <p>The <em>Results</em> directory contains three subdirectories and the script <em>Models_Outputs.R</em>. The <em>Results/Fitted_models</em> directory includes all .RData files with fitted models for each species. The script <em>Models_Outputs.R </em>generates all outputs (Figures, Tables, Numbers) included in the paper and additional results in the Supplementary Information, except for Figure 1 and AUC values. For these, refer to Lasgorceux et al., Zenodo, <a href="https://doi.org/10.5281/zenodo.12544212">https://doi.org/10.5281/zenodo.12544212</a>. The plots are stored in the <em>Results/Plots </em>folder, while <em>Results/RData</em> contains intermediate .RData files created by <em>Models_Outputs.R</em> to manage computational costs.</p>
FIGURE 2. Protected areas reporting odonates from 2001 in Odonata from protected areas in Colombia with new records and description of Cora verapax sp. nov. (Zygoptera: Polythoridae)
FIGURE 2. Protected areas reporting odonates from 2001 to 2017 in Colombia. a) Geographical distribution of the sampled areas. Polygons for SFF, RNSC, RFPN and No Register Reserves are too small to be noticed at the map scale. b) Number of sampled areas under the categories recognized by the SINAP.
FIGURE 1 in Odonata from protected areas in Colombia with new records and description of Cora verapax sp. nov. (Zygoptera: Polythoridae)
FIGURE 1. Colombian National System of Protected Areas (SINAP) including the register Civil Society Natural Reserves reported to the Ministry of Environment until 2015.
FIGURE 4 in Odonata from protected areas in Colombia with new records and description of Cora verapax sp. nov. (Zygoptera: Polythoridae)
FIGURE 4. Cora verapax sp. nov. holotype: a. head and thorax in dorsal and lateral views respectively; b. genital ligula in ventral view; c. S10 and cercus in dorsal view; d. S9–10 and cercus in lateral view; e. habitus in lateral view. a-l. p.: apicolateral processes, f. l. l.: filamentous lateral lobes, m-l. p.: midlateral processes. Photos: a, c–e: CABS; b: Camilo Flórez.
FIGURE 3 in Odonata from protected areas in Colombia with new records and description of Cora verapax sp. nov. (Zygoptera: Polythoridae)
FIGURE 3. Taxonomical distribution of odonates species reported in Colombian protected areas a) literature compilation from 2001 to 2017 and new records reported in this work b) new records based on six protected areas surveyed in this study. Numbers at the end of the bars correspond to the number of species.
FIGURE 3 in Nine new species of the " aeruginosus" - group in Amynthas (Clitellata: Megascolecidae) from Nam Et-Phouley National protected Area, Laos
FIGURE 3. Amynthas fleischmani sp. nov. (A,B), Amynthas antethecus sp. nov. (C,D), and Amynthas elenabondae sp. nov. (E,F). A,C,E: ventral view; B,D,F: spermatheca. Scale bars 2 mm.
FIGURE 2 in Nine new species of the " aeruginosus" - group in Amynthas (Clitellata: Megascolecidae) from Nam Et-Phouley National protected Area, Laos
FIGURE 2. Amynthas nametensis sp. nov. (A,B), Amynthas somechanae sp. nov. (C,D), and Amynthas wiggeri sp. nov. (E,F). A,C,E: ventral view; B,D,F: spermatheca. Scale bars 2 mm.
FIGURE 1 in Nine new species of the " aeruginosus" - group in Amynthas (Clitellata: Megascolecidae) from Nam Et-Phouley National protected Area, Laos
FIGURE 1. Amynthas bouatongi sp. nov. (A,B), Amynthas hoauykanangensis sp. nov. (C,D), and Amynthas phimpheti sp. nov. (E,F). A,C,E: ventral view; B,D,F: spermatheca. Scale bars 2 mm.
Protected areas in Greece (ICCS)
<p>Protected zones in Greece dataset provided by Terranis</p>
Input data and scripts for "Spatial conservation prioritization for the East Asian islands: a balanced representation of multi-taxon biogeography in a protected area network"
<p>This release contains the input files 'input_data.zip' for the spatial conservation prioritization analysis by Zonation software, which are conducted in Lehtomäki et al. Input data includes biodiversity features (species distribution maps from vascular plants, mammals, birds, reptiles, amphibians, and freshwater fishes), habitat condition map (human influence index), priority mask information (the categorized protected area distribution) and the Japanese prefecture polygons in GeoTiff format, and the list of species attributes for conservation weighting in CSV format. Note that endangered rare species have been excluded from this dataset, though they were reflected in the output files. The Zonation setting files and R scripts for pre- and post analyses are included in 'japan-zsetup-1.0.zip' and also placed at GitHub : https://github.com/cbig/japan-zsetup</p> <p>The output files (priority score maps and removal curves) from the original Zonation analyses are summarized in 'output_from_original.data.zip'</p>
FIGURE 1 in Stink bugs (Hemiptera, Heteroptera, Pentatomidae) of the Catimbau National Park, a protected area in Brazil's largest dry forest
FIGURE 1. Collection sites of Pentatomidae in Brazil sampled with systematized collection (A) focuses mainly in the Atlantic Forest of northeastern and southern Brazil and the Pampa (B–C). This study is the first systematized sampling of Pentatomidae in the Caatinga (C). AL, Alagoas; PE, Pernambuco; RS, Rio Grande do Sul; SC, Santa Catarina.
FIGURE 3 in Stink bugs (Hemiptera, Heteroptera, Pentatomidae) of the Catimbau National Park, a protected area in Brazil's largest dry forest
FIGURE 3. Dorsal habitus of species of Pentatomidae collected at the Catimbau National Park, Pernambuco, Brazil. (A) Podisus nigrispinus; (B) Tetragonotum megacephalum; (C) Edessa rufomarginata; (D) Edessa triangularis; (E) Edessa sp.; (F) Chinavia runaspis; (G) Cyptocephala alvarengai; (H) Dichelops (Diceraeus) caatinguensis; (I) Loxa deducta; (J) Mormidea v-luteum; (K) Piezodorus guildinii; (L) Thyanta humilis. Scale bars = 2 mm.
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Allen Brain Atlas
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
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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.