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Figure 4 in New records and geographic range extension of Epilobocera capolongoi Pretzmann, 2000 (Decapoda: Brachyura: Epiloboceridae) in Cuba, with notes on its natural history and conservation
Figure 4. Adult male Epilobocera capolongoi (CZACC 5.0047) (A–G) and adult male E. cubensis (CZACC 5.0050) (H–N) from Lomas de Banao Ecological Reserve. A, H, Habitus, dorsal view; B, I, habitus, ventral view; C, J, carapace, dorsal view; D, K, carapace, frontal view; E, L, third maxilliped; F, M, sternal surface; G, N, pleon. All the images were taken soon after death (keeping the coloration in life), except E and L (after preservation). The white outline in A and B represent the missing second and third left walking legs. Scale bars = 10 mm.
Figure 5 in New records and geographic range extension of Epilobocera capolongoi Pretzmann, 2000 (Decapoda: Brachyura: Epiloboceridae) in Cuba, with notes on its natural history and conservation
Figure 5. Adult female Epilobocera capolongoi (CZACC 5.0045) (A–D) and subadult female E. cubensis (CZACC 5.0059) (E–H) from Lomas de Banao Ecological Reserve. A, E, Habitus, dorsal view; B, F, habitus, ventral view; C, D, G, H, sternal surface, with detail of the vulvae (D, H). All the images were taken soon after death (keeping the coloration in life), except H (after preservation). Scale bars = 10 mm.
Figure 1 in New records and geographic range extension of Epilobocera capolongoi Pretzmann, 2000 (Decapoda: Brachyura: Epiloboceridae) in Cuba, with notes on its natural history and conservation
Figure 1. Distribution of Epilobocera capolongoi (circles) and E. cubensis (triangles) in central Cuba, depicting the previous records (orange circles) and new records (red circles) of E. capolongoi: 1) Tributary source of Higuanojo river, 2) La Sabina ranger station, 3) tributary source of Banao river, and 4) Banao river, near María Antonia ranger station; the westernmost new record (above) corresponds with Pico San Juan Ecological Reserve. Green shadings and contours depict protected areas. The two-headed orange arrow depicts the narrow strip of heights connecting the Trinidad Heights in the west and the Sancti Spíritus Heights in the east, assumed here as a putative communication pathway between the two presumably allopatric subpopulations of E. capolongoi.
Figure 2 in New records and geographic range extension of Epilobocera capolongoi Pretzmann, 2000 (Decapoda: Brachyura: Epiloboceridae) in Cuba, with notes on its natural history and conservation
Figure 2. Localities where Epilobocera capolongoi was collected in Lomas de Banao Ecological Reserve. Upper left, tributary source of Banao river; upper right, tributary source of Higuanojo river. Lower left, Banao river, near María Antonia ranger station. Lower right, view from La Sabina ranger station, after a heavy rain.
Conservation outcomes of dietary transitions across different values of nature - model outputs
<p>Archive of output reports produced for the MAgPIE v4.8.2 paper <strong>Conservation outcomes of dietary transitions across different values of nature</strong>.</p> <p><strong>Data</strong></p> <p>The data contain the MAgPIE model and post-processing outputs for all assessed scenarios, including the sensitivity test across the SSP1 and SSP3 scenarios.</p> <ul> <li>The file <em>rev9_healthyLscps_AOH_full_report.Rds </em>contains the outputs of our Area of Habitat (AOH) assessment for all assessed species and across all scenarios. The summary statistics shown in Figure 2 and Figure 3 have been derived from this data set. The data has also been used to create Extended Data Figures<span lang="EN-GB"> 5-</span>7<span lang="EN-GB"> and is shown in the Supplementary Information. </span>However, for Extended Data Figure<span lang="EN-GB"> 7</span> the data was <span lang="EN-GB">used in combination</span> with <span lang="EN-GB">rasterized </span>range polygons obtained from the <span lang="EN-GB">IUCN Red List Database (IUCN 2020).</span></li> <li><span lang="EN-GB">The file <em>rev9_healthyLscps_pollSuff_report_all.Rds </em>reports the global and regional cropland area (Mha) that is subject to insufficient and sufficient pollination supply. This is specified in the column ‘poll_class’, where 1 is insufficient and 2 is sufficient pollination supply. The data is shown in Figure 4, Extended Data Figure 8 and the Supplementary Information.</span></li> <li><span lang="EN-GB">The file <em>rev9_healthyLscps_RUSLE_report_all.Rds</em> reports estimated global and regional soil loss in Pg per year across all modelled scenarios. The data is displayed in Figure 4, Extended Data Figure 9 and the Supplementary Information.</span></li> <li><span lang="EN-GB">The file <em>rev9_healthyLscps_allSSP_report.rds </em>contains regional and global output variables from the MAgPIE model used in this study. The data is shown in Figure 1 and 5, as well as in Extended Data Figures 2-4 and the Supplementary Information.</span></li> <li><span lang="EN-GB">The file <em>rev9_healthyLscps_validation.rds </em>contains validation data for the MAgPIE model output variables.</span></li> </ul> <p> </p> <p><strong><span lang="EN-GB">Model code</span></strong></p> <p>The model code of the MAgPIE and SEALS models can be accessed via:</p> <p><em>MAgPIE model code</em><em>:</em></p> <ul> <li><a href="https://doi.org/10.5281/zenodo.13833444">https://doi.org/10.5281/zenodo.13833444</a> and <a href="https://github.com/magpiemodel/magpie">https://github.com/magpiemodel/magpie</a></li> </ul> <p><em>MAgPIE model documentation</em><em>:</em></p> <ul> <li><a href="https://rse.pik-potsdam.de/doc/magpie/4.3.5/">https://rse.pik-potsdam.de/doc/magpie/4.8.2/</a></li> </ul> <p><em>SEALS model code</em><em>:</em></p> <ul> <li><a href="https://github.com/jandrewjohnson/seals_dev/releases/tag/v1.0.0">https://github.com/jandrewjohnson/seals_dev/releases/tag/v1.0.0</a></li> </ul> <p><em>SEALS mode documentation:</em></p> <ul> <li><a href="https://justinandrewjohnson.com/earth_economy_devstack/seals_overview.html">https://justinandrewjohnson.com/earth_economy_devstack/seals_overview.html</a></li> </ul> <p> </p> <p><strong><span lang="EN-GB">Cited references</span></strong></p> <p><span>IUCN. (2020). <em>The IUCN Red List of Threatened Species. Version 2020-2</em>. https://www.iucnredlist.org.</span><em><span> </span></em><span>Downloaded on 25 November 2020</span></p>
Supplementary material 2 from: Trochet A, Schmeller D (2013) Effectiveness of the Natura 2000 network to cover threatened species. Nature Conservation 4: 35-53. https://doi.org/10.3897/natureconservation.4.3626
Supplementary material 2 from: Trochet A, Schmeller D (2013) Effectiveness of the Natura 2000 network to cover threatened species. Nature Conservation 4: 35-53. https://doi.org/10.3897/natureconservation.4.3626
Supplementary material 1 from: Gruber B, Evans D, Henle K, Bauch B, Schmeller D, Dziock F, Henry P, Lengyel S, Margules C, Dormann C (2012) "Mind the gap!" – How well does Natura 2000 cover species of European interest? Nature Conservation 3: 45-62. https://doi.org/10.3897/natureconservation.3.3732
The table shows the 54 gap species ordered by species group. Please note: The comment column is based on expert opinion of the European Topic Centre, which has the latest version of the Natura2000 data base and also knowledge on confidential sites, which are deleted from the public version of the data base to protect rare species.
Supplementary material 1 from: Schmeller D, Maier A, Evans D, Henle K (2012) National responsibilities for conserving habitats – a freely scalable method. Nature Conservation 3: 21-44. https://doi.org/10.3897/natureconservation.3.3710
The annex does provide a more detailed comparison of the different biogeographic maps. It further gives a list of all forest habitats given in the EU Habitats Direction
Supplementary material 1 from: Schmeller D, Henle K, Loyau A, Besnard A, Henry P (2012) Bird-monitoring in Europe – a first overview of practices, motivations and aims. Nature Conservation 2: 41-57. https://doi.org/10.3897/natureconservation.2.3644
The questionnaire was designed to assess how biodiversity monitoring schemes were carried out and what the motivation was to launch that scheme.
Supplementary material 1 from: Pontoppidan M, Nachman G (2013) Changes in behavioural responses to infrastructure affect local and regional connectivity – a simulation study on pond breeding amphibians. Nature Conservation 5: 13-28. https://doi.org/10.3897/natureconservation.5.4611
Full model description following the ODD-template suggested by Grimm et al. (2006, 2010) and model parameterisation. (doi: 10.3897/natureconservation.5.4611.app). File format: Adobe PDF document (pdf).:
Supplementary material 1 from: Bongard C, Butler K, Fulthorpe R (2013) Investigation of fungal root colonizers of the invasive plant Vincetoxicum rossicum and co-occurring local native plants in a field and woodland area in Southern Ontario. Nature Conservation 4: 55-76. https://doi.org/10.3897/natureconservation.4.3578
Supplementary material 1 from: Bongard C, Butler K, Fulthorpe R (2013) Investigation of fungal root colonizers of the invasive plant Vincetoxicum rossicum and co-occurring local native plants in a field and woodland area in Southern Ontario. Nature Conservation 4: 55-76. https://doi.org/10.3897/natureconservation.4.3578
Supplementary material 1 from: Pontoppidan M, Nachman G (2013) Spatial Amphibian Impact Assessment – a management tool for assessment of road effects on regional populations of Moor frogs (Rana arvalis). Nature Conservation 5: 29-52. https://doi.org/10.3897/natureconservation.5.4612
Full model description following the protocol suggested by Grimm et al. (2006, 2010) and model parameterisation. (doi: 10.3897/natureconservation.5.4612.app). File format: Adobe PDF document (pdf).:
Fig. 2 in Climatic niche, natural history, and conservation status of the Porthole Treefrog, Charadrahyla taeniopus (Günther, 1901) (Anura: Hylidae) in Mexico
Fig. 2. Current (A), and future 2050 (B) and 2070 (C) scenarios of the climatic niche of Charadrahyla taeniopus in Sierra Madre Oriental province (degraded area). The color scale indicates the probability of occupancy for the species.
Fig. 1 in Climatic niche, natural history, and conservation status of the Porthole Treefrog, Charadrahyla taeniopus (Günther, 1901) (Anura: Hylidae) in Mexico
Fig. 1. Female individual of Charadrahyla taeniopus (A) in a cloud forest and (B) at Tenango de Doria, Hidalgo, Mexico. Photos by Uriel Hernández-Salinas (A) and Raciel Cruz-Elizalde (B).
Figure 5 in The avifauna of Biak Island, Papua, Indonesia with comments on status, conservation, natural history and taxonomy
Figure 5. Tahiti Petrel Pseudobulweria rostrata or Beck's Petrel P. becki, between Biak and Numfor, 5 July 2017 (© Daniel Lopez-Velasco)
Figure 1 in The avifauna of Biak Island, Papua, Indonesia with comments on status, conservation, natural history and taxonomy
Figure 1. Teluk (Bay) Cenderawasih showing the principal islands and relationship with mainland New Guinea.
Figure 12 in The avifauna of Biak Island, Papua, Indonesia with comments on status, conservation, natural history and taxonomy
Figure 12. Little Shrikethrush Colluricincla megarhyncha, Biak, 5 July 2017 (© Daniel Lopez-Velasco)
Figure 14 in The avifauna of Biak Island, Papua, Indonesia with comments on status, conservation, natural history and taxonomy
Figure 14. Biak Leaf Warbler Seicercus misoriensis, Biak, November 2010; note the lack of an obvious pale supercilium, dull coloration and, especially, the relatively long flesh-coloured bill and brightly coloured legs (© Mikael Bauer)
Fig. 1 in Non-volant mammals of the 'Lago di Tarsia' Regional Nature Reserve and Special Conservation Area (IT93100055; Cosenza, Southern Italy)
Fig. 1 - Land use map of the study area (Source: Brusco et al., 2017). Grid corresponds to 1x1 km squares. Black line: border of the 'Lago di Tarsia' Regional Nature Reserve and Special Conservation Area (IT93100055; Cosenza, Southern Italy). On the right: black circle represents the location along Italian peninsula. / Carta dell'uso del suolo dell'area di studio. Linea scura: confine della Riserva Naturale Regionale "Lago di Tarsia" e Zona Speciale di Conservazione (IT93100055; Cosenza, Italia meridionale). Sulla sinistra: la localizzazione nella penisola italiana.
Fig. 2 in Houseflies speaking for the conservation of natural areas: a broad sampling of Muscidae (Diptera) on coastal plains of the Pampa biome, Southern Brazil
Fig. 2. Sample coverage curves based on the number of individuals of Muscidae per region in the Coastal Plain (CPPB) of Rio Grande do Sul, Brazil. The grey shaded area represents the confidence intervals. (a) region 1; (b) region 2; (c) region 3; (d) region 4; (e) region 5; (f) CPPB total.
ScienceDex guides
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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.