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1,549 results for “invertebrate”

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zenodo28/100

Figure 1 from: Knight L, Brancelj A, Hänfling B, Cheney C (2015) The groundwater invertebrate fauna of the Channel Islands. Subterranean Biology 15: 69-94. https://doi.org/10.3897/subtbiol.15.4792

Figure 1 - The location of the Channel Islands in the English Channel (map from Robins et al. 2012).

opencc-by-4.0May 2015View details →
zenodo28/100

Figure 5 from: Simões MH, Souza-Silva M, Ferreira RL (2015) Cave physical attributes influencing the structure of terrestrial invertebrate communities in Neotropics. Subterranean Biology 16: 103-121. https://doi.org/10.3897/subtbiol.16.5470

Figure 5 - Non-metric multidimensional scaling (Jaccard index) using presence and absence of species sampled in 55 limestone caves of the Brazilian Savannah. The figure shows that the cave, despite dry most of the year, is subject to seasonal flooding (Deus Me Livre cave), and then was more similar to caves with streams.

opencc-by-4.0Nov 2015View details →
zenodo28/100

Figure 4 from: Simões MH, Souza-Silva M, Ferreira RL (2015) Cave physical attributes influencing the structure of terrestrial invertebrate communities in Neotropics. Subterranean Biology 16: 103-121. https://doi.org/10.3897/subtbiol.16.5470

Figure 4 - Correlation between the richness of troglomorphic species and linear development and water body presence/absence. The barr represents the average and the trace the standard deviation. Different letters indicate significant differences in average richness.

opencc-by-4.0Nov 2015View details →
zenodo28/100

Figure 3 from: Simões MH, Souza-Silva M, Ferreira RL (2015) Cave physical attributes influencing the structure of terrestrial invertebrate communities in Neotropics. Subterranean Biology 16: 103-121. https://doi.org/10.3897/subtbiol.16.5470

Figure 3 - Correlation between total richness and width of entrances, linear development and water body presence/absence. The barr represents the average and the trace the standard deviation. Different letters indicate significant differences in average richness.

opencc-by-4.0Nov 2015View details →
zenodo28/100

Figure 1 from: Simões MH, Souza-Silva M, Ferreira RL (2015) Cave physical attributes influencing the structure of terrestrial invertebrate communities in Neotropics. Subterranean Biology 16: 103-121. https://doi.org/10.3897/subtbiol.16.5470

Figure 1 - Cave distribution at Minas Gerais state, Brazil (black triangle), where terrestrial invertebrates were sampled.

opencc-by-4.0Nov 2015View details →
zenodo28/100

Figure 1 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 1 - Distribution of 15 caves in the Atlantic Forest in the state of Espírito Santo, with invertebrate fauna inventoried in this study. Source: SOS Mata Atlântica (2011).

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 8 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 8 - Human alterations in caves of Espírito Santo, Brazil. A religious use in granite cave in Venda Nova dos Imigrantes B transformation of granitic cave into a church in Itaimbé-Itaguassu C deforestation surrounding cave in Ecoporanga, D drainage exploitation in granite cave near Pedro Canário E use of cave as goat corral F road construction destroying cave chambers in Vargem Alta G and I Limoeiro cave entrance with religious and tourist use in Conceição de Castelo H using limestone cave as a timber-yard in Vargem Alta.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 7 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 7 - Almost significant differences between the diversity and total and relative richness of invertebrates in caves that develop in carbonate rocks and magma in the state of Espírito Santo. Average, ± SE, ± SD.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 3 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 3 - Some of the troglomorphic invertebrates sampled in 15 caves in Atlantic forest at Espírito Santo state, Brazil. A Escadabiidae, B Trachelipodidae, C Pseudonannolene sp., D Cryptodesmidae, E Trichopolidesmydae, F Zygentoma, G Trichorhina sp.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 2 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 2 - Composition and richness of invertebrate taxa collected in 15 caves in the state of Espírito Santo, Brazil.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 6 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 6 - A Significant relationship of the increased richness of collected invertebrates with the increase in size of caves in limestone and granitic rocks and B no significant relationship without limestone caves in the state of Espírito Santo.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 9 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 9 - A Distribution of cave biological relevance B cave impacts category and C cave fauna vulnerability in the state of Espírito Santo. Gray shading on maps represents remnants of the Atlantic Forest.

opencc-by-4.0Aug 2015View details →
zenodo28/100

Figure 5 from: Souza-Silva M, Ferreira RL (2015) Cave invertebrates in Espírito Santo state, Brazil: a primary analysis of endemism, threats and conservation priorities. Subterranean Biology 16: 79-102. https://doi.org/10.3897/subtbiol.16.5227

Figure 5 - A Distribution of caves, B relative richness and C total richness of the 15 caves of the state of Espírito Santo, Brazil.

opencc-by-4.0Aug 2015View details →
zenodo28/100

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).

opencc-by-4.0Mar 2016View details →
zenodo28/100

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.

opencc-by-4.0Mar 2016View details →
zenodo28/100

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.

opencc-by-4.0Mar 2016View details →
zenodo28/100

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.

opencc-by-4.0Mar 2016View details →
zenodo28/100

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.

opencc-by-4.0Mar 2016View details →
zenodo28/100

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.

opencc-by-4.0Mar 2016View details →
zenodo28/100

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).

opencc-by-4.0Mar 2016View details →

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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.

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OpenNeuro

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Last verified 2026-04-29Open record