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Stable Isotope Hydrology Data from Gnamma Systems in the Colorado Front Range
<p>This dataset accompanies a submission to Geophysical Research Letters titled "Stable Isotopes Constrain Water Seepage from Gnammas into Bare Granitic Bedrock".</p>
Global warming pushes the distribution range of the two alpine 'glasshouse' Rheum species north- and upwards in the Eastern Himalayas (EH) and the Hengduan Mountains (HM)
<p><span>Alpine plants' distribution is being pushed higher towards mountaintops due to global warming, finally diminishing their range and thereby increasing the risk of extinction. Plants with specialized 'glasshouse' structures have adapted well to harsh alpine environments, notably to the extremely low temperatures, which makes them vulnerable to global warming. </span><span>How</span><span>ever, their response to global warming is quite unexplored. Therefore, by compiling occurrences and several environmental strata, we utilized multiple ensemble species distribution modeling (eSDM) to estimate the historical, present-day, and future distribution of two alpine 'glasshouse' species <em>Rheum nobile</em> Hook. f. & Thomson and <em>R. alexandrae</em> Batalin. <em>Rheum nobile</em> was predicted to extend its distribution from the Eastern Himalaya (EH) to the Hengduan Mountains (HM), whereas <em>R. alexandrae</em> was restricted exclusively in the HM. Both species witnessed a northward expansion of suitable habitats followed by a southerly retreat in the HM region. Our findings reveal that both species have a considerable range shift under different climate change scenarios, mainly triggered by precipitation rather than temperature. The model predicted northward and upward migration for both species since the last glacial period which is mainly due to expected future climate change scenarios. Further, the observed niche overlap between the two species presented that they are more divergent depending on their habitat, except for certain regions in the HM. However, relocating appropriate habitats to the north and high elevation may not ensure the species' survival, as it needs to adapt to the extreme climatic circumstances in alpine habitats. Therefore, we advocate for more conservation efforts in these biodiversity hotspots.</span></p>
Data from: Predicting range shifts of the giant pandas under future climate and land use scenarios
<p><span><strong>Aim</strong>:</span><span> Understanding and predicting how species will respond to global environmental change (i.e., climate and land use change) is essential to efficiently inform conservation and management strategies for authorities and managers. Here, we assessed the combined effect of future climate and land use change on the potential range shifts of the giant pandas (<em>Ailuropoda melanoleuca</em>). </span></p> <p><span><strong>Location</strong>:</span><span> Sichuan Province, China.</span></p> <p><span><strong>Methods</strong>: </span><span>We used ensemble species distribution models (SDMs) to forecast range shifts of the giant pandas by the 2050s and 2070s under four combined climate and land use change scenarios. We also</span><span> compared the differences in </span><span>distributional changes of giant pandas among the five mountains in the study area. </span></p> <p><span><strong>Results</strong>: </span><span>Our ensemble SDMs exhibited good model performance in terms of both AUC (0.931) and TSS (0.747), and suggested that precipitation seasonality, annual mean temperature, the proportion of forest cover and total annual precipitation are the most important factors in shaping the current distribution patterns for the giant pandas. Our projections of future species distribution also suggested a range expansion under an optimistic greenhouse gas emission, while suggesting a range contraction under a pessimistic greenhouse gas emission. Moreover, we found that there is considerable variation in the projected range change patterns among the five mountains in the study area. Especially, the suitable habitat of the giant panda is predicted to increase under all scenarios in Minshan mountains, while is predicted to decrease under all scenarios in Daxiangling and Liangshan mountains, indicating the vulnerability of the giant pandas at low latitudes. </span></p> <p><span><strong>Main conclusions</strong>: </span><span>Our findings highlight the importance of an integrated approach that combines climate and land use change to predict the future species distribution and the need for a spatial explicit consideration of the projected range change patterns of target species for guiding conservation and management strategies. </span></p>
Elevational range of mammals, birds, and amphibians in the Himalayas
<p><span>The lowest and highest elevations known for each species are used to delineate its elevational limits. We assume that species potentially exist between their elevational limits. For species that have a single elevational distribution record (resulting in an elevational range of zero) as well as those with elevational ranges less than 200 m, we adjusted their elevation ranges to 200 m. We verified all data for accuracy by experts within the region and any dubious outlying records were removed. Elevational limits were given for 1,488 species, including 314 mammals, 1027 birds, and 147 amphibians in the Himalayas.</span></p>
Figs 1–4 in A new species of the genus Cymindis Latreille, 1805 (Coleoptera: Carabidae: Lebiini) from the Kunlun Mt. Range, China
Figs 1–4. Cymindis (Iscariotes) kalabi sp. n. 1 – holotype, male, habitus, dorsal view; 2 –
Figure 6 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 6. (A) Prosopodesmus jacobsoni, gonopod in mesal view (after Silvestri, 1910); (B) Glyphiulus granulatus, anterior gonopods in posterior view; (C) Trachyjulus calvus, anterior gonopods in anterior view; (D) Trachyjulus calvus, posterior gonopods in anterior view (after Schubart, 1946); (E) Leptogoniulus sorornus, anterior gonopods in anterior view; (F) Leptogoniulus sorornus, telopodite of left posterior gonopod in anterior view (after Shelley & Lehtinen, 1999). Scale bars: 20 µm (B); 100 µm (C, D); 750 µm (E); 1 mm (F). Image (A) not to scale.
Figure 5 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 5. (A) Oxidus gracilis, gonopod in mesal view; (B) Orthomorpha coarctata, gonopod in mesal view; (C) Trigoniulus corallinus, anterior gonopods in anterior view; (D) Trigoniulus corallinus, telopodite of left posterior gonopod in anterior view; (E) Rhinotus purpureus, anterior gonopod in posterior view; (F) Rhinotus purpureus, posterior gonopod in posterior view. Scale bars: 100 µm (A, B, E, F); 750 µm (C); 1 mm (D).
Figure 3 in Extending the geographic and altitudinal range of Popilius gibbosus (Burmeister, 1847) (Coleoptera: Passalidae) with taxonomical comments
Figure 3. Geographical distribution of Popiliusgibbosus (Burmeister, 1847) in South America, with previous and new records.
Figure 3 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 3. Introduced species in Brazil: (A) Brazilian regions; (B) Proportion of species by states and regions; (C) Richness by grid 1°×1°. See Table 1 for the abbreviations of the states.
Figure 4 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 4. Introduced species in Brazil, habitus: (A) Orthomorpha coarctata; (B) Oxidus gracilis; (C, D) Glyphiulus granulatus; (E) Trigoniulus corallinus; (F) Rhinotus purpureus. Scale bars: 2 mm (A, B, E); 500 µm (C, D); 200 µm (F).
Figure 2 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 2. Distribution maps of Trigoniulus corallinus, Leptogoniulus sorornus (Spirobolida, Pachybolidae), Cylindroiulus truncorum (Julida, Julidae), Paraspirobolus lucifugus (Spirobolida, Spirobolellidae), and Rhinotus purpureus (Polyzoniida, Siphonotidae).
Figure 2 in Extending the geographic and altitudinal range of Popilius gibbosus (Burmeister, 1847) (Coleoptera: Passalidae) with taxonomical comments
Figure 2. Popilius gibbosus (Burmeister, 1847). (A) Head and prothorax, dorsal; (B) Head, ventral (C) Head and prothorax, dorsolateral; (D) Prosternal process and mesosternum; (E) Metasternum (left side); (F) Aedeagus (ventral, dorsal and lateral view).
Figure 1 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 1. Distribution maps of Oxidus gracilis, Orthomorpha coarctata (Polydesmida, Paradoxosomatidae), Prosopodesmus jacobsoni (Polydesmida, Haplodesmidae), Glyphiulus granulatus (Spirostreptida, Cambalopsidae), Trachyjulus calvus (Spirostreptida, Cambalopsidae), Epitrigoniulus cruentatus (Spirobolida, Pachybolidae), and Cylindroiulus britannicus (Julida, Julidae).
Figure 7 in A preliminary survey and range extension of millipedes species introduced in Brazil (Myriapoda, Diplopoda)
Figure 7. (A) Epitrigoniulus cruentatus, anterior gonopods in posterior view (after Brölemann, 1903); (B) Epitrigoniulus cruentatus, posterior gonopods in anterior view (after Brölemann, 1903). Distal region in detail; (C) Paraspirobolus lucifugus, anterior gonopods in anterior view; (D) Paraspirobolus lucifugus, posterior gonopod in anterior view (after Attems, 1900); (E) Cylindroiulus britannicus, gonopod in anterior view. Detail of telson in lateral view (after Blower, 1985); (F) Cylindroiulus truncorum, gonopod in anterior view (after Blower, 1985). Images not to scale.
Figure 2 in 35 years behind the scenes: range extension of the rare Gro's manticore, Morunasaurus groi (Squamata, Hoplocercidae), in Colombia
Figure 2. Morunasaurus groi in life. (A) Adult male from Dabeiba municipality, Antioquia Department (ICN 6101). (B) Adult female from San Carlos municipality, Antioquia (MHUA-R 13735). Notice the sexual dimorphism in throat coloration. Male's photo courtesy of Juan M. Renjifo.
Figure 1 in 35 years behind the scenes: range extension of the rare Gro's manticore, Morunasaurus groi (Squamata, Hoplocercidae), in Colombia
Figure 1. Distribution map of Morunasaurus groi. Yellow symbols are previous records from literature (Dunn, 1933; Corredor et al., 1985; Torres-Carvajal et al., 2011), while red is the new one here presented. Triangle is the type locality. Green polygons are the protected areas in Colombia from SINAP open data (Sistema Nacional de Áreas Protegidas, in Spanish).
Figure 4 in 35 years behind the scenes: range extension of the rare Gro's manticore, Morunasaurus groi (Squamata, Hoplocercidae), in Colombia
Figure 4. Morunasaurus groi in life from Valle de Antón, Panama (type locality). (A-B) Adult males, (C-D) adult females. Photos: Cesar Barrio-Amorós (A-C), Josh Vandermeulen (D).
Figure 3 in 35 years behind the scenes: range extension of the rare Gro's manticore, Morunasaurus groi (Squamata, Hoplocercidae), in Colombia
Figure 3. Dorsal (A) and ventral (B) coloration of Morunasaurus groi from the Magdalena's river basin. Photographs were taken post-mortem but immediately after to the euthanasia.
Historical Arabidopsis thaliana genomes from across its native range.
<p>We report short-read Illumina sequencing of 131 <em>Arabidopsis thaliana </em>herbarium specimens across its native range collected from 1820 to 2010. Sequencing depth averaged ~6X across these genomes. Sequences from the herbarium samples showed the expected degradation patterns typical of ancient DNA with endogenous DNA content between 18.01-88.26% (mean 56%; median 74%) and enrichment of cytosine to thymine substitutions at fragment ends. We provide access to the sequences upon request.</p>
Dispersal and coastal geomorphology limit potential for mangrove range expansion under climate change
<p>Latitudinal range limits for mangroves on high-energy, wave-dominated coasts are controlled by geomorphological features and estuarine dynamics. Mangroves reach a southern global range limit along the South African coastline, but the distribution is patchy, with stands occurring in only 16% of the estuaries in the region. Yet, the persistence of forests planted >50 years ago beyond the natural distribution limit suggests that additional estuaries could support mangroves. Understanding regional drivers is necessary to inform global scale estimates for how this important ecosystem is predicted to respond to climate change.</p> <p>Here, we combine species distribution modeling (MaxEnt), Lagrangian particle tracking using an eddy- and tide-resolving numerical ocean model, and connectivity matrices, to identify suitable mangrove habitats at present, as well as under the IPCC RCP4.5 and RCP8.5 climate scenarios.</p> <p>Within the current South African distribution range (± 900 km), eight more estuaries were identified as suitable under contemporary conditions. When considering potential range extension (± 110 km), an additional 14 suitable estuaries were identified. Connectivity matrices suggest limited long-distance dispersal, stranding mostly at or near the release location, and a decreased probability of connectivity towards the range limit. Under both future climate scenarios, 30% of estuaries currently supporting mangroves are predicted to become unsuitable, while an additional six estuaries beyond the current distribution are predicted to become suitable. However, there is limited connectivity between these new sites and established forests.</p> <p><em>Synthesis</em>: This study shows that dispersal substantially limits mangrove distribution at the southern African range limit and highlights the importance of including this process in species distribution models. Ultimately, our results provide new insight for mangrove conservation and management at range limits that are not controlled predominantly by temperature, as it has been assumed that mangroves will largely expand to higher latitudes under climate change.</p>
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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.