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National Checklists: Germany Species List
Data from: GBIF.org (23 January 2025) GBIF Occurrence Download <a href="https://doi.org/10.15468/dl.vd2ajk" target="_blank" rel="noopener">https://doi.org/10.15468/dl.vd2ajk</a>
Fleshy red algae mats act as temporary reservoirs for sessile invertebrate biodiversity - Raw data for biodiversity analysis, species list and detailed output data from iNEXT procedure
<p>Raw data for biodiversity analysis, species list and detailed output data from iNEXT procedure for manuscript entitled "Fleshy red algae mats act as temporary reservoirs for sessile invertebrate biodiversity".</p>
Distribution. Java. Several biogeographic reviews failed to list the genus for Bali, an island directly east of Java with strong biogeographic affinities to the latter. A sighting was, however, reported from Bali Barat National Park, in a birdwatching trip report. Given the live-animal trade of this species on Java, further records are needed to confirm whether or not there is a native population of the genus on Bali. If there is, biogeographic considerations suggest it would be most closely related to the Javan population and quite probably conspecific. in Tragulidae
Distribution. Java. Several biogeographic reviews failed to list the genus for Bali, an island directly east of Java with strong biogeographic affinities to the latter. A sighting was, however, reported from Bali Barat National Park, in a birdwatching trip report. Given the live-animal trade of this species on Java, further records are needed to confirm whether or not there is a native population of the genus on Bali. If there is, biogeographic considerations suggest it would be most closely related to the Javan population and quite probably conspecific.
Fig. 3 in Towards Target 1 of the Global Strategy for Plant Conservation: A working list of all known plant species - Progress and prospects
Fig. 3. Proportions of listed and unlisted species in the different distribution patterns. Numbers of listed species derived from online working lists; estimates of species numbers in families without working lists estimated from Stevens (2006).
Appendix. The status of global taxonomic checklist preparation for flowering plant families (based on Angiosperm Phylogeny Group II but modified to reflect circumscriptions of existing checklists). If a checklist is complete and available on the Internet then the URL is also given. The species numbers (sp. no.) given are either based on actual working lists (WL) where they exist or are based on Stevens (2006) if no WL is available. Five categories are used to describe the status of a particular working list: 1, checklist complete and accessible via the Internet now; 2, checklist available on Internet by end of 2007 (Asteraceae 2010); 3, checklist complete but not online; 4, some online lists giving partial coverage may be available; 5, no global checklist being compiled so far as known. in Towards Target 1 of the Global Strategy for Plant Conservation: A working list of all known plant species - Progress and prospects
Appendix. The status of global taxonomic checklist preparation for flowering plant families (based on Angiosperm Phylogeny Group II but modified to reflect circumscriptions of existing checklists). If a checklist is complete and available on the Internet then the URL is also given. The species numbers (sp. no.) given are either based on actual working lists (WL) where they exist or are based on Stevens (2006) if no WL is available. Five categories are used to describe the status of a particular working list: 1, checklist complete and accessible via the Internet now; 2, checklist available on Internet by end of 2007 (Asteraceae 2010); 3, checklist complete but not online; 4, some online lists giving partial coverage may be available; 5, no global checklist being compiled so far as known.
Fig. 1 in Towards Target 1 of the Global Strategy for Plant Conservation: A working list of all known plant species - Progress and prospects
Fig. 1. Graph of line of number of accepted species plotted against number of species names. Line of best fit: y = 0.395x–88.53; R2 = 0.97.
Notes on Fomitiporia Murrill in Amazon region: a list of species and new references
<p>Twenty-three specimens of fungi of genus <i>Fomitiporia</i> Murrill, collected in the Amazonian region in the states of Amazonas and Roraima in their respective rainy periods were analyzed. The present study has both resulted in the description of eight species, namely <i>F. apiahyna s. l. </i>(Speg.) Robledo, Decock & Rajchenb<i>.</i>, <i>F. calkinsii </i>(Murrill) Vlasák & Kout, <i>F. conyana </i>Alves-Silva & Drechsler-Santos<i>, F. impercepta </i>Morera, Robledo&Urcelay, <i>F. langloisii </i>Murrill, <i>F. maxonii </i>Murrill, <i>F. murrillii </i>Alves-Silva, R.M. Silveira & Drechsler-Santos<i> </i>and <i>F. neotropica </i>Camp.-Sant., Amalfi, R.M. Silveira, Robledo & Decock contributed with new records for the Amazonian region, Brazil and the Americas.</p>
Assessing the population genetic structure of introduced rainbow trout (Oncorhynchus mykiss) in the Lake Tahoe basin: A case for understanding hybridization potential during the reintroduction of the native Endangered Species Act listed Lahontan cutthroat trout (O. clarkii henshawi)
<p class="MsoNormal">Hybridization with introduced or invasive species is a major threat and driver of population declines in native salmonids. The rainbow trout (<em>Oncorhynchus mykiss</em>, RBT) has been widely introduced globally and represents an important invasive species, often establishing entrenched naturalized populations. The cutthroat trout (<em>Oncorhynchus clarkii</em>, CT), a close congener, is particularly susceptible to competition and hybridization from RBT introductions which has led to range-wide population declines and loss of CT genetic variation. The Lahontan CT (<em>O. c. henshawi</em>, LCT) whose historic distribution included the Lake Tahoe basin, was extirpated by the 1940s due to overfishing and introduction of nonnative salmonids, including now naturalized RBT. Here, we characterize genetic variation of RBT in a subset of Lake Tahoe tributaries to assess potential homing of RBT to streams for spawning, thereby informing LCT reintroduction. Diploid reproductively viable RBT were stocked annually into Lake Tahoe from the late 1800s until the mid-2000s by California and Nevada fish and wildlife agencies, planting the same commonly raised hatchery strains over time. Since 2007, triploid RBT comprise the bulk of RBT planted. Despite extensive dispersal from stocking locations, our analyses revealed variation in population differentiation among tributaries, with individuals from spatially proximate streams clustering across multiple population genetic analyses. Although subtle, we detected evidence for genetic differentiation among tributaries from the southern, western, and northern regions, including surprising structure involving a single tributary. These results illustrate the extent of differentiation within and among streams and could inform possibilities for and implications of RBT removal and LCT reintroduction.</p>
FIGURE 2 in Cynosurus peltieri (Pooideae, Poaceae), a poorly known species endemic to the Algerian-Tunisian terrestrial flora: further insights on its occurrence, IUCN Red List assessment, and lectotypification
FIGURE 2. Cynosurus polybracteatus in its habitat in Kroumirian area. A. Habit of the plant. B–C. Details of its unilateral and linear, indistinctly lobed panicle, with very short branches. All photographs were taken by Ridha El Mokni in Tabarka (Jendouba, NW of Tunisia, North Africa), 14 May 2013 and 3 May 2017.
FIGURE 1 in Cynosurus peltieri (Pooideae, Poaceae), a poorly known species endemic to the Algerian-Tunisian terrestrial flora: further insights on its occurrence, IUCN Red List assessment, and lectotypification
FIGURE 1. Cynosurus peltieri in its typical habitat in Kroumirian oak forests. A. Habit of the plant. B. Detail of its unilateral and linear, clearly lobed panicle. All photographs were taken by Ridha El Mokni in Aîn Zana-Aîn Draham (Jendouba, NW of Tunisia, North Africa), 16 June 2020.
Distribution. Confirmed from NW Africa, the Sahel, and Nile Valley, E through the Middle East and WArabia to NW& C India (E to E Madhya Pradesh, 80° E); with possible distribution spots in E & SE India (indicated byfour mostlyhistorical records). Reportedly common in Bangladesh (yet disproved by recent reports) and retained on species lists of Myanmar, Thailand, and Sumatra without being supported by anyrecent record. in Rhinopomatidae
Distribution. Confirmed from NW Africa, the Sahel, and Nile Valley, E through the Middle East and WArabia to NW& C India (E to E Madhya Pradesh, 80° E); with possible distribution spots in E & SE India (indicated byfour mostlyhistorical records). Reportedly common in Bangladesh (yet disproved by recent reports) and retained on species lists of Myanmar, Thailand, and Sumatra without being supported by anyrecent record.
Distribution. Known from two localities in SW Ecuador (El Oro Province); more recently, it has been recorded in the Pacific coast of Colombia (Choco and Valle del Cauca departments), and NW Peru (Tumbes Department). Known distribution is changing as existing specimens from NW South America (listed as S. Lilium parvidens) are reidentified as this species; new geographic and ecological information is being gathered in the process, and it could be locally common at some specific habitats. in Phyllostomidae
Distribution. Known from two localities in SW Ecuador (El Oro Province); more recently, it has been recorded in the Pacific coast of Colombia (Choco and Valle del Cauca departments), and NW Peru (Tumbes Department). Known distribution is changing as existing specimens from NW South America (listed as S. Lilium parvidens) are reidentified as this species; new geographic and ecological information is being gathered in the process, and it could be locally common at some specific habitats.
Distribution. NE Madagascar, extremely limited distribution in the far N of the island, just to the S of Antsiranana (= Diégo-Suarez), it was formerly believed to inhabit both dry and humid forests from the Montagne d' Ambre region S to the Mahavavy River near Ambilobe in the W, and probably to the Fanambana River S of Vohémarin the E. However, with the recognition of the Ankarana Sportive Lemur (L. ankaranensis) as a distinct species, the range of the Sahafary Sportive Lemur was reduced to a handful of very small remnant forest patches nearthe villages of Madirobe and Ankarongana in the Sahafary region, and in the immediate vicinity of Andrahona, a small mountain rising out of the surrounding lowlands about 30 km south of Antsiranana and E of the RN6 main road. Recent faunal surveys in the Montagne des Francais, a calcareous massif of c.6114 ha approximately 12 km SE of Antsiranana, listed the Sahafary Sportive Lemur as one of the species occurring there, but this needs to be confirmed; it may be widerranging than the Ankarana Sportive Lemur. in Lepilemuridae
Distribution. NE Madagascar, extremely limited distribution in the far N of the island, just to the S of Antsiranana (= Diégo-Suarez), it was formerly believed to inhabit both dry and humid forests from the Montagne d' Ambre region S to the Mahavavy River near Ambilobe in the W, and probably to the Fanambana River S of Vohémarin the E. However, with the recognition of the Ankarana Sportive Lemur (L. ankaranensis) as a distinct species, the range of the Sahafary Sportive Lemur was reduced to a handful of very small remnant forest patches nearthe villages of Madirobe and Ankarongana in the Sahafary region, and in the immediate vicinity of Andrahona, a small mountain rising out of the surrounding lowlands about 30 km south of Antsiranana and E of the RN6 main road. Recent faunal surveys in the Montagne des Francais, a calcareous massif of c.6114 ha approximately 12 km SE of Antsiranana, listed the Sahafary Sportive Lemur as one of the species occurring there, but this needs to be confirmed; it may be widerranging than the Ankarana Sportive Lemur.
The first comprehensive revision of all the species attributed to Melomys led J. I. Menzies in 1996 to resurrect the genus Paramelomys and to redefine its morphologicallimits and species content. Menzies created P. gressitti as a new species belonging to a group displaying morphological similarities and including also P. lorentzii and P. moncktoni. Monotypic Distribution. E New Guinea. Descriptive notes. Head-body 135-162 mm, hindfoot 30-34 mm; no specific data are available for body weight. Gressitt's Mosaic-tailed Rat is a medium-sized Paramelomys with a soft, thick and woolly pelage, a long narrow foot, and a tail with three hairs per scale. It exhibits a medium-sepia dorsal pelage and a gray-buff ventral one. Tail is slightly shorter (99%) than head-body length. The skull has a narrow zygomatic plate. Habitat. Moist tropical mountain forest between 2300 m and 2400 m. Food and Feeding. No information. Breeding. No information. Activity patterns. Gressitt's Mosaic-tailed Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List owing to its small geographic range (less than 3500 km?*) and the destruction ofits habitat by mining and logging activities. The major threat to Gressitt's Mosaic-tailed Rat is ongoing habitat degradation caused by nearby human populations; habitat on Mount Kandy has been destroyed by gold-miners and wood-cutters. Bibliography. Menzies (1996). in Muridae
The first comprehensive revision of all the species attributed to Melomys led J. I. Menzies in 1996 to resurrect the genus Paramelomys and to redefine its morphologicallimits and species content. Menzies created P. gressitti as a new species belonging to a group displaying morphological similarities and including also P. lorentzii and P. moncktoni. Monotypic Distribution. E New Guinea. Descriptive notes. Head-body 135-162 mm, hindfoot 30-34 mm; no specific data are available for body weight. Gressitt's Mosaic-tailed Rat is a medium-sized Paramelomys with a soft, thick and woolly pelage, a long narrow foot, and a tail with three hairs per scale. It exhibits a medium-sepia dorsal pelage and a gray-buff ventral one. Tail is slightly shorter (99%) than head-body length. The skull has a narrow zygomatic plate. Habitat. Moist tropical mountain forest between 2300 m and 2400 m. Food and Feeding. No information. Breeding. No information. Activity patterns. Gressitt's Mosaic-tailed Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List owing to its small geographic range (less than 3500 km?*) and the destruction ofits habitat by mining and logging activities. The major threat to Gressitt's Mosaic-tailed Rat is ongoing habitat degradation caused by nearby human populations; habitat on Mount Kandy has been destroyed by gold-miners and wood-cutters. Bibliography. Menzies (1996).
Lophuromys medicaudatus, L. woosnami, and L. luteogaster are in subgenus Kivumys and woosnami species group. Monotypic. Distribution. Endemic to the Albertine Rift, occurring around Lake Kivu in E DR Congo and Rwanda and SW Uganda (Bwindi). Descriptive notes. Head—body 92-112 mm, tail 73-95 mm, ear 15-19 mm, hindfoot 18-23 mm; weight 29-43 g. Similar to other species in subgenus Kivumys, the Western Rift Brush-furred Rat has unspeckled pelage, and tail ¢.85% of head-body length. Dorsum is uniform dark brown-olive, and venter is orange. Females have three pairs of mammae. Habitat. Mountain swamps and mountain forests at elevations of 1850-2500 m. Food and Feeding. The Western Rift Brush-furred Rat is omnivorous; diets contain 30-100% arthropods, mollusks, seeds, and fruits. Breeding. Female Western Rift Brush-furred Rats can have 1-2 embryos. Pregnant females were observed in February, April, and July. Activity patterns. The Western Rift Brush-furred Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Vulnerable on The IUCN Red List. The Western Rift Brush-furred Rat has never been found in modified secondary environment and is quite rare. Bibliography. Dieterlen (1976b, 1987 2013g), Kasangaki et al. (2003), Verheyen et al. (1996). in Muridae
Lophuromys medicaudatus, L. woosnami, and L. luteogaster are in subgenus Kivumys and woosnami species group. Monotypic. Distribution. Endemic to the Albertine Rift, occurring around Lake Kivu in E DR Congo and Rwanda and SW Uganda (Bwindi). Descriptive notes. Head—body 92-112 mm, tail 73-95 mm, ear 15-19 mm, hindfoot 18-23 mm; weight 29-43 g. Similar to other species in subgenus Kivumys, the Western Rift Brush-furred Rat has unspeckled pelage, and tail ¢.85% of head-body length. Dorsum is uniform dark brown-olive, and venter is orange. Females have three pairs of mammae. Habitat. Mountain swamps and mountain forests at elevations of 1850-2500 m. Food and Feeding. The Western Rift Brush-furred Rat is omnivorous; diets contain 30-100% arthropods, mollusks, seeds, and fruits. Breeding. Female Western Rift Brush-furred Rats can have 1-2 embryos. Pregnant females were observed in February, April, and July. Activity patterns. The Western Rift Brush-furred Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Vulnerable on The IUCN Red List. The Western Rift Brush-furred Rat has never been found in modified secondary environment and is quite rare. Bibliography. Dieterlen (1976b, 1987 2013g), Kasangaki et al. (2003), Verheyen et al. (1996).
Species list of Collembola known to display ecomorphosis (extended)
<p>This dataset presents an extended species list of ecomorphic species in Collembola.<br> New species and/or update of species already present can be made in the future upon proper literature references and/or <em>in situ</em> observations.<br> <br> <strong>Related research article</strong>: This species list is a complement to the Table 1 that can be found in<br> Bonfanti et al. (2023) Ecomorphosis in European Collembola: a review in the context of trait-based ecology. <em>Applied Soil Ecology</em>, Volume 182, 104692. <a href="https://doi.org/10.1016/j.apsoil.2022.104692">https://doi.org/10.1016/j.apsoil.2022.104692</a> </p> <p>If you aim to contribute or if you need further information, please contact jonathan.bonfanti[at]gmail[dot]com </p> <p>If this dataset was useful for your works/research, please give a proper citation of the related research article.</p>
Species list, with traits, in four forest types
<p>Ecological strategy is the tactics employed by species in adapting to abiotic and biotic conditions. Ecological strategy spectrum is defined as the relative proportion of species in different ecological strategy types within a community. Determinants of ecological strategy spectrum of plant community explored by most previous studies are about abiotic factors. Yet, the roles of biotic factors in driving variations of ecological strategy spectra of forest communities across different geographic regions remains unknown. Here, we established 200 0.04-ha forest dynamics plots and measured three leaf functional traits of tree and shrub species in four forest vegetation types across four climatic zones. Based on Grime's CSR triangular framework and the StrateFy method, we categorized species into four ecological strategy groups (C-, S-, Int-, and R-groups) and related the ecological spectra of the forests to three species diversity indices (species richness, Shannon Wiener index, and stem density (stem abundance)). Linear-regression, redundancy analysis and variance partition analysis were utilized for assessing the roles of species diversity in regulating ecological strategy spectra of forest communities across different climatic zones. We found that the proportion of species in the C- and Int-groups increased, while that in the S-group decreased, with the increase of three indices of species diversity. Among the three species diversity indices, stem abundance played the most important role in driving variations in ecological strategy spectra of forests across different climatic zones. Our finding highlights the necessity of accounting for biotic factors, especially stem abundance, in modeling or predicting the geographical distributions of plant species with varied ecological adaptation strategies to future environmental changes.</p>
Supplementary material 1 from: De Meyer M, Delatte H, Mwatawala M, Quilici S, Vayssières J-F, Virgilio M (2015) A review of the current knowledge on Zeugodacus cucurbitae (Coquillett) (Diptera, Tephritidae) in Africa, with a list of species included in Zeugodacus. In: De Meyer M, Clarke AR, Vera MT, Hendrichs J (Eds) Resolution of Cryptic Species Complexes of Tephritid Pests to Enhance SIT Application and Facilitate International Trade. ZooKeys 540: 539-557. https://doi.org/10.3897/zookeys.540.9672
Genus Zeugodacus (Diptera, Tephritidae), list of valid species: Explanation note: This list includes species listed under subgenera Asiadacus; Austrodacus; Diplodacus; Hemigymnodacus, comb. n.; Heminotodacus; Hemiparatridacus; Nesodacus; Niuginidacus; Papuodacus; Paradacus; Parasinodacus, comb. n.; Sinodacus; and Zeugodacus.
Supplementary material 1 from: Janion-Scheepers C, Deharveng L, Bedos A, Chown SL (2015) Updated list of Collembola species currently recorded from South Africa. ZooKeys 503: 55-88. https://doi.org/10.3897/zookeys.503.8966
Table S1: Explanation note: Collection details of Collembola recorded from continental South Africa.
FIGURE 2. Marmara viburnella male genitalia. 2a in A new species of Marmara (Lepidoptera: Gracillariidae: Marmarinae), with an Annotated List of Known Hostplants for the Genus
FIGURE 2. Marmara viburnella male genitalia. 2a, Genital capsule with valvae, ventral view. 2b, Phallus, lateral view.
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.