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1,118 results for “subterranean biology”
Figure 13 from: Katz AD, Taylor SJ, Soto-Adames FN, Addison A, Hoese GB, Sutton MR, Toulkeridis T (2016) New records and new species of springtails (Collembola: Entomobryidae, Paronellidae) from lava tubes of the Galápagos Islands (Ecuador). Subterranean Biology 17: 77-120. https://doi.org/10.3897/subtbiol.17.7660
Figure 13 - Pseudosinella intermixta syntypes. A syntype specimen chosen for slide mount (INHS Acc. 567,409) B hind claw complex C detail of preservation condition of syntypes in ethanol D original labels in vial.
Figure 2 from: Katz AD, Taylor SJ, Soto-Adames FN, Addison A, Hoese GB, Sutton MR, Toulkeridis T (2016) New records and new species of springtails (Collembola: Entomobryidae, Paronellidae) from lava tubes of the Galápagos Islands (Ecuador). Subterranean Biology 17: 77-120. https://doi.org/10.3897/subtbiol.17.7660
Figure 2 - A Drip pool in dark zone of Cueva Chato 2 (Santa Cruz Island, Galápagos Islands, Ecuador), where Pseudosinella vulcana sp. n. was collected from surface film. Photo by SJT, 15 March 2014 B Entrance of Cueva Cañón (Santa Cruz Island, Galápagos Islands, Ecuador), where Lepidocyrtus nigrosetosus was collected. Photo by SJT, 10 March 2014.
Figure 10 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 10 - Scatterplots showing the relationship between stygofauna taxon richness per sample and different physico-chemical variables; In Figure 10 the scatterplots presented are based on available data in the Queensland Subterranean Aquatic Fauna database where: depth to groundwater is available for 113 samples in meters below ground level (mbgl); electrical conductivity is available for 137 samples in microSiemens per centimetre (μS/cm); pH is available for 130 samples; and temperature is available for 77 samples in degrees Celsius (°C).
Figure 5 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 5 - Biogeography of described families in Queensland, Australia; In Figure 5 the total number of subregions a described family has been recorded inhabiting is indicated by numerical figures located to the right of the bars and the total number of samples is indicated by numerical figures located along the y-axis.
Figure 4 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 4 - Stygofauna discovery rates by lithology in Queensland, Australia; In Figure 4 the discovery rate of stygofauna is indicated by numerical figures located above the columns, the total number of samples is indicated by numerical figures located along the x-axis, and the average stygofauna discovery rate (28%) is plotted as a grey, dashed line.
Figure 8 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 8 - Distribution of described families across different lithologies in Queensland, Australia; In Figure 8 the total number of lithologies is indicated by numerical figures located to the right of the bars and the total number of samples is indicated by numerical figures located along the y-axis.
Figure 7 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 7 - Diversity of described families across different lithologies in Queensland, Australia; In Figure 7 the total number of described families is indicated by numerical figures located above the columns and the total number of samples is indicated by numerical figures located along the x-axis.
Figure 6 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 6 - Diversity of described families in different IBRA subregions in Queensland, Australia; In Figure 6 the total number of described families is indicated by numerical figures located to the right of the bars and the total number of samples is indicated by numerical figures located along the y-axis.
Figure 9 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 9 - Comparison of systemic composition of described families from Australia and the World Average; In Figure 9 the systemic composition of described stygofauna families is compared between the Pilbara region (Western Australia, Australia) derived from Eberhard et al. (2005), Queensland (Australia), and the World Average derived from Eberhard et al. (2005).
Figure 3 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 3 - Distribution of stygofauna sampling effort by lithology in Queensland, Australia; In Figure 3 the total number of samples is indicated by numerical figures located above the columns and the percentage of samples is indicated by numerical figures along the x-axis.
Figure 2 from: Glanville K, Schulz C, Tomlinson M, Butler D (2016) Biodiversity and biogeography of groundwater invertebrates in Queensland, Australia. Subterranean Biology 17: 55-76. https://doi.org/10.3897/subtbiol.17.7542
Figure 2 - Outline map of Queensland, Australia highlighting the location of stygofauna sampling sites and other localities; In Figure 2 an outline map shows the location of all 582 stygofauna sampling sites and other key localities mentioned in the text (e.g. Bowen Basin, Murray–Darling Basin, Proserpine–Sarina Lowlands IBRA region).
Figure 6 from: Taylor SJ, Niemiller ML (2016) Biogeography and conservation assessment of Bactrurus groundwater amphipods (Crangonyctidae) in the central and eastern United States. Subterranean Biology 17: 1-29. https://doi.org/10.3897/subtbiol.17.7298
Figure 6 - Human population density (2010 U.S. Census from the U.S. Census Bureau) by county with ranges for the eight Bactrurus species. For Bactrurus brachycaudus, Bactrurus hubrichti, and Bactrurus mucronatus, the range boundary has been interpreted as in Fig. 5.
Figure 1 from: Taylor SJ, Niemiller ML (2016) Biogeography and conservation assessment of Bactrurus groundwater amphipods (Crangonyctidae) in the central and eastern United States. Subterranean Biology 17: 1-29. https://doi.org/10.3897/subtbiol.17.7298
Figure 1 - Distribution of species of the genus Bactrurus (Amphipoda, Crangonyctidae) in relation to karst. Karst areas are based on Weary and Doctor (2014). Letters A–F (red arrows) are localities discussed in the body of the text.
Figure 5 from: Taylor SJ, Niemiller ML (2016) Biogeography and conservation assessment of Bactrurus groundwater amphipods (Crangonyctidae) in the central and eastern United States. Subterranean Biology 17: 1-29. https://doi.org/10.3897/subtbiol.17.7298
Figure 5 - Species ranges for the genus Bactrurus (Amphipoda, Crangonyctidae) in relation to pre-Pleistocene rivers of the mid-western United States. Shaded areas with thin dashed lines represent species ranges. For Bactrurus brachycaudus, Bactrurus hubrichti and Bactrurus mucronatus, the range boundary has been interpreted in light of these rivers. Heavy dashed line is maximum extent of Pleistocene glaciation.
Figure 4 from: Taylor SJ, Niemiller ML (2016) Biogeography and conservation assessment of Bactrurus groundwater amphipods (Crangonyctidae) in the central and eastern United States. Subterranean Biology 17: 1-29. https://doi.org/10.3897/subtbiol.17.7298
Figure 4 - Groundwater amphipod relationships modified after the maximum clade credibility diagram of Corrigan et al. (2014) with 95% highest posterior density intervals shown as gray bars, and with additional details of geological timeline following Cohen et al. (2013).
Figure 3 from: Taylor SJ, Niemiller ML (2016) Biogeography and conservation assessment of Bactrurus groundwater amphipods (Crangonyctidae) in the central and eastern United States. Subterranean Biology 17: 1-29. https://doi.org/10.3897/subtbiol.17.7298
Figure 3 - Land use within the ranges of the eight species of the genus Bactrurus. Based on the National Land Cover Database (Homer et al. 2015), collapsed into six categories (see Methods).
Figure 2 from: Taylor SJ, Niemiller ML (2016) Biogeography and conservation assessment of Bactrurus groundwater amphipods (Crangonyctidae) in the central and eastern United States. Subterranean Biology 17: 1-29. https://doi.org/10.3897/subtbiol.17.7298
Figure 2 - Distribution of species of the genus Bactrurus (Amphipoda, Crangonyctidae), overlain on a map of the maximum extent of Pleistocene glacial episodes derived from Fullerton et al. (2003). Letters A–F (red arrows) are localities discussed in the body of the text.
Figure 2 from: de Ázara LN, Bernardi LFO, Ferreira RL (2016) The first survey on harvestmen in Brazilian artificial cavities, with notes on distribution and natural history. Subterranean Biology 17: 31-53. https://doi.org/10.3897/subtbiol.17.6762
Figure 2 - Artificial cavities in: A, B, C Alagoa D and E Padre Paraíso F Caraí G Mariana H São José da Safira I Caeté J Mariana.
Figure 1 from: de Ázara LN, Bernardi LFO, Ferreira RL (2016) The first survey on harvestmen in Brazilian artificial cavities, with notes on distribution and natural history. Subterranean Biology 17: 31-53. https://doi.org/10.3897/subtbiol.17.6762
Figure 1 - Map of the state of Minas Gerais, Brazil, showing the biomes and municipalities in which the artificial cavities are situated: a Alagoa b Ataléia c Caeté d Caraí e Mariana f Mateus Leme g Medina h Nova Lima i Novo Oriente de Minas j Ouro Preto k Padre Paraíso l São José da Safira m Vazante.
Figure 5 from: de Ázara LN, Bernardi LFO, Ferreira RL (2016) The first survey on harvestmen in Brazilian artificial cavities, with notes on distribution and natural history. Subterranean Biology 17: 31-53. https://doi.org/10.3897/subtbiol.17.6762
Figure 5 - Mitogoniella mucuri inside the Túnel do Garrafão (Alagoa) A Female guarding eggs on the wall of the mine B Female guarding immatures on the wall of the mine.
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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
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