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Fig. 10. Pillarakaruah n in The "Striped" Group of Stiphidiid Spiders: Two New Genera from Northeastern New South Wales, Australia (Araneae: Stiphidiidae: Amaurobioidea)
Fig. 10. Pillarakaruah n.sp. (a,b) Malepalp (KS34509): (a) ventral, (b) retrolateral. (c–e) Femaleepigynum (KS70337): (c) ventral, (d) lateral, (e) dorsal-internal genitalia. Scale line 0.5 mm.
FIGURE 2 in First Report of Sabella spallanzanii (Gmelin, 1791) (Annelida: Polychaeta) from Botany Bay, New South Wales, a northern range extension for the invasive species within Australia
FIGURE 2. Diagnostic features of Sabella spallanzanii. A, branchial crown emerging from tube, showing colour pattern. Live specimen from Botany Bay (one from AM W43464), photo by S. Humphreys. B, branchial crown showing asymmetric lobes. Preserved specimen (AM W24270, from North Haven, South Australia), photo by E. Wong. C, junction of thorax and abdomen showing: a, thoracic companion chaetae; b, spiralled fascicle of abdominal chaetae. Live specimen from Botany Bay (one from AM W43464), photo by S. Humphreys.
FIGURE 1 in First Report of Sabella spallanzanii (Gmelin, 1791) (Annelida: Polychaeta) from Botany Bay, New South Wales, a northern range extension for the invasive species within Australia
FIGURE 1. Map showing collecting location of Sabella spallanzanii in Botany Bay. Inset: recorded locations of S. spallanzanii populations in Australia. = Botany Bay. X = Port Adelaide. = Port Phillip Bay. A = Devonport. □ = Eden Harbour (Twofold Bay). ● = Esperance. Ο = Bunbury. ♢ = Albany. ♦ = Spencer Gulf. ̝= Cockburn Sound and Fremantle.
Fig. 6 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 6. (a, b) Output from morphometric analysis of 29 characters measured from 20 specimens of Prostanthera, showing three discrete groups. (a) Flexible unweighted pair-group method with arithmetic mean (UPGMA) phenogram, with yellow line indicating dissimilarity value; (b)semi-strong hybrid multidimensional scaling (SSHMDS) ordination with characters, with PCC vectors with R2 values of>0.9, with the size of each sphere representing its position in three-dimensional space (stress = 0.0503). See Supplementary Table S2 for OTU codes, Supplementary Table S3 for character list, and Supplementary Table S5 for PCC values.
Fig. 5 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 5. Individual ancestry proportions from model-based clustering by using sNMF of all sampled individuals for values of K = 2–8. Putative species groups are labelled. Sample codes follow those outlined in Supplementary Table S1.
Fig. 3 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 3. Neighbour-network graph produced by SplitsTree5 of DArTseq SNP data of samples remaining following the exclusion of clones. Putative species groups are coloured, and populations are labelled. NP, National Park; NR, Nature Reserve.
Fig. 4 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 4. Phylogeny generated by SVDquartets analysis of DArTseq SNP data for 27 samples of Prostanthera. Putative species groups are coloured, and popula-tions are labelled. Labels are species/ phrase names and population of origin, followed by primary collector and collection number.
Fig. 2 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 2. Three-dimensional (3-D) plot of principalcomponent analysis (PCA) of DArTseq SNP data of samples remaining following the exclusion of clones, showing PCA1 v. PCA2 v. PCA3. NP, National Park; NR, Nature Reserve.
Fig. 8 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 8. Photograph images of Prostanthera volucris. (a) Habitat and associated vegetation; (b) habit; (c) habit, close-up; (d) flower and bud. Images: R. P. O'Donnell.
Fig. 1 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 1. Occurrence records of Prostanthera gilesii, P. phylicifolia sens. str. and the Evans Crown population obtained from Australia's Virtual Herbarium (2021) after removal of misidentified records and accessions of P. phylicifolia s. lat. as identified by O'Donnell et al. (2021). Populations sampled in this study for genomic analysis (Supplementary Table S1) are indicated with larger, transparent circles, and populations with associated herbarium vouchers that were measured for morphological phenetic analysis (Supplementary Table S2) are indicated with crosses.
Fig. 7 in Molecular and morphological analyses support recognition of Prostanthera volucris (Lamiaceae), a new species from the Central Tablelands of New South Wales
Fig. 7. Illustration of Prostanthera volucris. (a) Habit; (b) detail of branch surface, showing retrorse trichomes; (c) leaf surface, abaxial view; (d) detail of abaxial leaf lamina surface, showing midrib and indumentum; (e) leaf lamina surface, adaxial view; (f) flower, lateral view, showing calyx, prophyll, corolla, anthers; (g) flower, ventral view, showing corolla inner surface of lobes and tube, stamens, and style; (h) stamen, showing ventral view of anther locules, connective appendage and distal portion of staminal filament; (i) stamen, showing dorsal view of anther, connective appendage and distal portion of staminal filament; (j) mericarp, ventral view, showing abscission scar. Illustration: R. P. O'Donnell.
Subspecies and Distribution. M. e. erminea Linnaeus, 1758 — Finland, Norway, NW Russia, and Sweden. M. e. aestiva Kerr, 1792 — most of mainland N & C Europe to C Asia in Kazakhstan, Kyrgyzstan, and Tajikistan. M. e. alascensis Merriam, 1896 — S Alaska. M. e. anguinae Hall, 1932 — SW Canada (Vancouver I, British Columbia). M. e. arctica Merriam, 1896 — Alaska and NW Canada. M. e. bangsi Hall, 1945 — C Canada and NC USA. M. e. celenda Hall, 1944 — Alaska (Prince of Wales I). M.e. cicognanii Bonaparte, 1838 — SE Canada and NE USA. M. e. fallenda Hall, 1945 — W Canada (British Columbia) and NW USA (N Washington). M. e. ferghanae Thomas, 1895 — Afghanistan, N India, and Pakistan. M.e. gulosa Hall, 1945 — NW USA (E Washington). M.e. haidarum Preble, 1898 — W Canada (Queen Charlotte Is, British Columbia). M.e. hibernica Thomas & Barrett-Hamilton, 1895 — Ireland. M.e. imatis Hall, 1944 — Alaska (Baranof I). M.e. invicta Hall, 1945 — SW Canada (Alberta) and NW USA (Idaho & Montana). M.e. kadiacensis Merriam, 1896 — Alaska (Kodiak I). M.e. kaneti Baird, 1857 — NE China, Russia (E Siberia). M.e. karaginensis Jurgenson, 1936 — NE Russia (Karaginsky I). M.e. lymani Hollister, 1912 — E Russia (Altai Mts, Siberia). M.e. minima Cavazza, 1912 — Switzerland. M.e. mongolica Ognev, 1928 — NW China and Mongolian Altai. M. e. muricus Bangs, 1899 — USA (N California, Colorado, Idaho, New Mexico, Nevada, Oregon, South Dakota, Utah & Wyoming). M. e. nippon Cabrera, 1913 — Japan. M.e. olympica Hall, 1945 — NW USA (Olympic Peninsula, Washington). M.e. polaris Barrett-Hamilton, 1904 — Greenland. M.e.richardsonii Bonaparte, 1838 — N Canada. M.e. ricinae G. S. Miller, 1907 — Scotland (Islay I). M.e.salva Hall, 1944 — SE Alaska (Admiralty I). M.e.seclusa Hall, 1944 — SE Alaska (Suemez I). M.e.sempler Sutton & Hamilton, 1932 — Canada (Franklin & Keewatin Districts). M.e.stabilis Barrett-Hamilton, 1904 — Great Britain. M.e.streatori Merriam, 1896 — W USA (NE California, Oregon & coastal Washington). M.e.teberdina Kornejv, 1941 — Russian Caucasus. M.e. tobolica Ognev, 1923 — W Siberia. Introduced to New Zealand. in Mustelidae
Subspecies and Distribution. M. e. erminea Linnaeus, 1758 — Finland, Norway, NW Russia, and Sweden. M. e. aestiva Kerr, 1792 — most of mainland N & C Europe to C Asia in Kazakhstan, Kyrgyzstan, and Tajikistan. M. e. alascensis Merriam, 1896 — S Alaska. M. e. anguinae Hall, 1932 — SW Canada (Vancouver I, British Columbia). M. e. arctica Merriam, 1896 — Alaska and NW Canada. M. e. bangsi Hall, 1945 — C Canada and NC USA. M. e. celenda Hall, 1944 — Alaska (Prince of Wales I). M.e. cicognanii Bonaparte, 1838 — SE Canada and NE USA. M. e. fallenda Hall, 1945 — W Canada (British Columbia) and NW USA (N Washington). M. e. ferghanae Thomas, 1895 — Afghanistan, N India, and Pakistan. M.e. gulosa Hall, 1945 — NW USA (E Washington). M.e. haidarum Preble, 1898 — W Canada (Queen Charlotte Is, British Columbia). M.e. hibernica Thomas & Barrett-Hamilton, 1895 — Ireland. M.e. imatis Hall, 1944 — Alaska (Baranof I). M.e. invicta Hall, 1945 — SW Canada (Alberta) and NW USA (Idaho & Montana). M.e. kadiacensis Merriam, 1896 — Alaska (Kodiak I). M.e. kaneti Baird, 1857 — NE China, Russia (E Siberia). M.e. karaginensis Jurgenson, 1936 — NE Russia (Karaginsky I). M.e. lymani Hollister, 1912 — E Russia (Altai Mts, Siberia). M.e. minima Cavazza, 1912 — Switzerland. M.e. mongolica Ognev, 1928 — NW China and Mongolian Altai. M. e. muricus Bangs, 1899 — USA (N California, Colorado, Idaho, New Mexico, Nevada, Oregon, South Dakota, Utah & Wyoming). M. e. nippon Cabrera, 1913 — Japan. M.e. olympica Hall, 1945 — NW USA (Olympic Peninsula, Washington). M.e. polaris Barrett-Hamilton, 1904 — Greenland. M.e.richardsonii Bonaparte, 1838 — N Canada. M.e. ricinae G. S. Miller, 1907 — Scotland (Islay I). M.e.salva Hall, 1944 — SE Alaska (Admiralty I). M.e.seclusa Hall, 1944 — SE Alaska (Suemez I). M.e.sempler Sutton & Hamilton, 1932 — Canada (Franklin & Keewatin Districts). M.e.stabilis Barrett-Hamilton, 1904 — Great Britain. M.e.streatori Merriam, 1896 — W USA (NE California, Oregon & coastal Washington). M.e.teberdina Kornejv, 1941 — Russian Caucasus. M.e. tobolica Ognev, 1923 — W Siberia. Introduced to New Zealand.
Health condition data for Platypus from New South Wales and Victoria
<p>Platypuses (<i>Ornithorhynchus anatinus</i>) inhabit the permanent rivers and creeks of eastern Australia, from north Queensland to Tasmania, but are experiencing multiple and synergistic anthropogenic threats. Baseline information of health is vital for effective monitoring of populations but is currently sparse for mainland platypuses. Focusing on six hematology and serum chemistry metrics as indicators of health and nutrition (packed cell volume (PCV), total protein (TP), albumin, globulin, urea, creatinine, and triglycerides), we investigated their variation across the species' range and across seasons. We analyzed 259 samples collected from platypuses in three river catchments in New South Wales and Victoria. Health metrics significantly varied across the species' range, with platypuses from the most northerly catchment, having lower levels of PCV, albumin and triglycerides, potentially reflecting thermal stress. The Snowy River showed significant seasonal patterns<b> </b>which varied between the sexes and coincided with differential reproductive stressors. Male creatinine and triglyceride levels were significantly lower than females, suggesting that reproduction is energetically more taxing on males. Age specific differences were also found, with juvenile PCV and TP levels significantly lower than adults. Additionally, the commonly used body condition index (tail volume index) was only negatively correlated with urea, and triglyceride levels. A meta-analysis of available literature <a>did not reveal any significant latitudinal relationship</a>, but this was confounded by variation in sampling times which is not commonly reported. We provide the first reference intervals of hematology and blood chemistry for mainland platypus, highlighting the importance of considering seasonal variation, enabling future assessments of individual and population health.</p>
Predicting habitat suitability for wild deer in relation to threatened ecological communities in south-eastern New South Wales, Australia
<p><strong>Context.</strong> High density deer populations can cause ecological damage, yet their distribution and impacts are poorly known across much of Australia. As a result, land managers rely on anecdotal reports to make decisions about management and control measures.</p> <p><strong>Aims.</strong> We aimed to model habitat suitability for deer in the South Coast of New South Wales (NSW), Australia, to be used as a baseline for future management and identify which threatened ecological communities (TECs) in the region are at greatest current risk of being occupied by deer.</p> <p><strong>Methods.</strong> We compiled 678 presence-only records of wild deer from online databases, observations made by National Parks and Wildlife Service field staff and field-based surveys. We combined these observations with eight environmental variables to model and map habitat suitability for deer across our study area using maximum entropy. Three spatial models of habitat suitability across our study area were produced: one for all deer species; and two species-specific models for fallow and sambar deer. Key results. Our models indicate that suitable habitat for deer exists throughout much of the South Coast of NSW. Of the TECs examined, Coastal Saltmarsh, Themeda Grassland, and Swamp Sclerophyll Forest had the highest proportion of area likely to be extremely suitable for deer and thus should be prioritised for protection within our study area.</p> <p><strong>Conclusions. </strong>Further systematic field-based surveys are needed to improve the quality of models in this region. Implications. We recommend that areas having high habitat suitability but are not yet occupied by deer be identified as sites where deer occupancy could be prevented.</p>
Distribution. SE Australia, in SE Queensland, New South Wales, Victoria, and SE South Australia; also Flinders I and Tasmania. in Vespertilionidae
Distribution. SE Australia, in SE Queensland, New South Wales, Victoria, and SE South Australia; also Flinders I and Tasmania.
Distribution. SW Western Australia, E & SE Queensland (including Fraser I), C & E New South Wales, Victoria, and SE South Australia, SW & E Australia. A specimen is known from Fiji, but this is suspected to represent the New Caledonian Long-eared Bat (NV. nebulosus) or a mislabeled specimen. in Vespertilionidae
Distribution. SW Western Australia, E & SE Queensland (including Fraser I), C & E New South Wales, Victoria, and SE South Australia, SW & E Australia. A specimen is known from Fiji, but this is suspected to represent the New Caledonian Long-eared Bat (NV. nebulosus) or a mislabeled specimen.
Distribution. Restricted to arid areas of inland Australia S of Tropic of Capricorn, in SW Western Australia, S Northern Territory, South Australia, SW Queensland, W New South Wales, and NW Victoria; distribution is disjunct, with Western Australian population isolated from C & E population by treeless areas of Nullarbor Plain. in Molossidae
Distribution. Restricted to arid areas of inland Australia S of Tropic of Capricorn, in SW Western Australia, S Northern Territory, South Australia, SW Queensland, W New South Wales, and NW Victoria; distribution is disjunct, with Western Australian population isolated from C & E population by treeless areas of Nullarbor Plain.
Distribution. Sparse and patchy distribution in arid and semiarid regions of Australia, extending E from C Australia to Great Dividing Range in Queensland and N New South Wales. in Molossidae
Distribution. Sparse and patchy distribution in arid and semiarid regions of Australia, extending E from C Australia to Great Dividing Range in Queensland and N New South Wales.
Distribution. SE Australia in three isolated populations: New South Wales (Kosciuszko National Park) and Victoria (a population between Mt Bogong and Mt Higginbotham and another distinct population on Mt Buller). in Burramyidae
Distribution. SE Australia in three isolated populations: New South Wales (Kosciuszko National Park) and Victoria (a population between Mt Bogong and Mt Higginbotham and another distinct population on Mt Buller).
Distribution. SE Australia, from the McPherson and Border ranges in SE Queensland, S to Victoria and SE South Australia; it is absent from the coastal drainages of the Great Dividing Range, S at least to the Wallamba River, and W of the Great Dividing Range in New South Wales (but it probably occurs to the limit of tree growth on the Southern Tableland), and from the inland draining catchments of the Murray Basin in Victoria. in Acrobatidae
Distribution. SE Australia, from the McPherson and Border ranges in SE Queensland, S to Victoria and SE South Australia; it is absent from the coastal drainages of the Great Dividing Range, S at least to the Wallamba River, and W of the Great Dividing Range in New South Wales (but it probably occurs to the limit of tree growth on the Southern Tableland), and from the inland draining catchments of the Murray Basin in Victoria.
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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)
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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.