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Fig. S2 in Evidence of genetic connectivity between fragmented pig populations in a tropical urban city-state
Fig. S2. Plot of Delta K from STRUCTURE output showing the Delta K values for the corresponding K values. The higher the Delta K value, the better the genetic structure is explained.
Fig. 4 in Evidence of genetic connectivity between fragmented pig populations in a tropical urban city-state
Fig. 4. Mean observed heterozygosities of the Northeast population and the Central Catchment Nature Reserve population. Error bars represent 95% confidence intervals of the mean.
Fig. 2. Principal Component Analysis plot showing the 42 in Evidence of genetic connectivity between fragmented pig populations in a tropical urban city-state
Fig. 2. Principal Component Analysis plot showing the 42 individuals from the Central Catchment Nature Reserve (CCNR) and the Northeast differentiated by sex and age class. Individuals exhibiting genetic admixture are labelled. Percentage variation accounted for by each principal component is indicated in brackets.
Fig. 1 in Evidence of genetic connectivity between fragmented pig populations in a tropical urban city-state
Fig. 1. Map of Singapore, in relation to Johor (Malaysia), showing various land-use types and the study sites (Central Catchment Nature Reserve, Northeast). Offshore islands Pulau Tekong and Pulau Ubin where pigs are also present are labelled. White stars indicate locations of cage traps.
Fig. S1. Principal Component Analysis plot showing 28 in Evidence of genetic connectivity between fragmented pig populations in a tropical urban city-state
Fig. S1. Principal Component Analysis plot showing 28 out of 42 individuals from the Central Catchment Nature Reserve (CCNR) and the Northeast with kinship values <0.2. Individuals are differentiated by sex and age class. Individuals exhibiting genetic admixture are labelled. Percentage variation accounted for by each principal component is indicated in brackets.
Fig. 3 in Evidence of genetic connectivity between fragmented pig populations in a tropical urban city-state
Fig. 3. STRUCTURE plot at K=2. Individuals are labelled according to 1) ID number, 2) sex and 3) age class (A for adult, J for juvenile). Sampling localities are indicated by brackets above the bars.
Text-fig. 13. Scanning electron microscope (SEM) images of pollen or spore clump with pollen grains or spores of unknown affinity that occur separately or adhering together in dyads, triads and tetrads; Torres Vedras locality, Portugal. a) Clump of pollen or spores that yielded the pollen or spores in this Text-figure; b–f) Grains adhering together in twos, threes or fours (b–e) or occurring singly and apparently with a proximal trilete mark (f); note that the adhering grains are connected by a smooth bandlike covering, perhaps remains of the microspore mother cell; note also abundant orbicules of various sizes among and over the grains. Specimen, TV44-S148149. Scale bars 300 Μm (a), 30 Μm (b–f). in The Early Cretaceous Mesofossil Flora Of Torres Vedras (Ne Of Forte Da Forca), Portugal: A Palaeofloristic Analysis Of An Early Angiosperm Community
Text-fig. 13. Scanning electron microscope (SEM) images of pollen or spore clump with pollen grains or spores of unknown affinity that occur separately or adhering together in dyads, triads and tetrads; Torres Vedras locality, Portugal. a) Clump of pollen or spores that yielded the pollen or spores in this Text-figure; b–f) Grains adhering together in twos, threes or fours (b–e) or occurring singly and apparently with a proximal trilete mark (f); note that the adhering grains are connected by a smooth bandlike covering, perhaps remains of the microspore mother cell; note also abundant orbicules of various sizes among and over the grains. Specimen, TV44-S148149. Scale bars 300 Μm (a), 30 Μm (b–f).
Fig. 2 in Fish larvae assemblages in two floodplain lakes with different degrees of connection to the Paraná River, Brazil
Fig. 2. Larvae abundances for the different species in Xambrê Lake (a) and Saraiva Lake (b) in Ilha Grande National Park, upper Paraná River, during the three studied spawning seasons.
Fig. 5 in Fish larvae assemblages in two floodplain lakes with different degrees of connection to the Paraná River, Brazil
Fig. 5. Sample scores of retained axes (Axes 1, 2, and 3) from the non-metric multidimensional scaling (NMS) controlling for sites (S1 - Saraiva channel, S2 - Saraiva middle, X1 - Xambrê stream and X2 - Xambrê middle) (a; b) and spawning seasons (I, II and III) (c; d). Variation of mean scores axis for sites (e) and spawning seasons (f) in Ilha Grande National Park, upper Paraná River (s.d. = standard deviation).
Fig. 4 in Fish larvae assemblages in two floodplain lakes with different degrees of connection to the Paraná River, Brazil
Fig. 4. Variations in mean species richness (number of species) (a), evenness (E) (b) and Shannon Diversity Index (H') (c) of fish larvae per sampling for Xambrê Lake and Saraiva Lake sites (S1 - Saraiva channel, S2 - Saraiva middle, X1 - Xambrê stream and X2 - Xambrê middle) in Ilha Grande National Park, upper Paraná River, during the three studied spawning seasons (s.d. = standard deviation).
Fig. 5. Correlation between PCA axis 1 in Fish assemblages of tropical floodplain lagoons: exploring the role of connectivity in a dry year
Fig. 5. Correlation between PCA axis 1 and species richness (a), density (b), and biomass (c) in connected [February (), May (), November ()] and disconnected lagoons, May (), August (), November ()]. Arrows indicate the direction of the limnological variables influence.
Fig. 4 in Fish assemblages of tropical floodplain lagoons: exploring the role of connectivity in a dry year
Fig. 4. DCA ordination of sample sites by month in connected [February (), May (), November ()] and disconnected lagoons [, May (), August (), November ()]. Arrows indicate the direction of influence of species in the ordination.
Fig. 2 in Fish assemblages of tropical floodplain lagoons: exploring the role of connectivity in a dry year
Fig. 2. Daily variation of pluviometric (a) and hydrometric levels (c) of the Paraná River in 2000, measured at Porto São José municipality, and difference between mean monthly pluviometric (b) and hydrometric levels (d) in 2000 (x) and the last 10 1 years (x). Data supplied by DNAEE (Departamento Nacional de Águas e Energia Elétrica). Dashed line indicates water level 2 required for initial inundation of the floodplain (Veríssimo, 1994).
Fig. 1 in Fish assemblages of tropical floodplain lagoons: exploring the role of connectivity in a dry year
Fig. 1. Study area with location of sampling sites in connected (1-6) and disconnected lagoons (7-15): 1 (Leopoldo),
Data from: Genetic diversity in a long-lived mammal is explained by the past's demographic shadow and current connectivity
<p>Within-species genetic diversity is crucial for the persistence and integrity of populations and ecosystems. Conservation actions require an understanding of factors influencing genetic diversity, especially in the context of global change. Both population size and connectivity are factors greatly influencing genetic diversity; the relative importance of these factors can however change through time. Hence, quantifying the degree to which population size or genetic connectivity are shaping genetic diversity, and at which ecological time scale (past or present), is challenging, yet essential for the development of efficient conservation strategies. In this study, we estimated the genetic diversity of 42 colonies of <i>Rhinolophus hipposideros,</i> a long-lived mammal vulnerable to global change, sampling locations spanning its continental northern range. We present an integrative approach that disentangles and quantifies the contribution of different connectivity measures in addition to contemporary colony size and historic bottlenecks in shaping genetic diversity. In our study, the best model explained 64% of the variation in genetic diversity. It included historic bottlenecks, contemporary colony sizes, connectivity and a negative interaction between the latter two. Contemporary connectivity explained most genetic diversity when considering a 65 km radius around the focal colonies, emphasizing the large geographic scale at which the positive impact of connectivity on genetic diversity is most profound and hence the minimum scale at which conservation should be planned. Our results highlight that the relative importance of the two main factors shaping genetic diversity varies through time, emphasizing the relevance of disentangling them to ensure appropriate conservation strategies.</p>
Identity Based Proxy Re-encryption Source Code for Security and Privacy in Connected Vehicle
<p>This is a source code for identity based proxy re-encryption using special string attribute for connected vehicle and Privacy, designed in python using Charm Cryptographic library using Pairing Group ss512 and 1024 bits.</p>
Figs 128–149 in Simulium (Trichodagmia) (Diptera, Simuliidae) phylogeny revisited: the Neotropical and Afrotropical connection
Figs 128–149. Larva (last instar). Postgenal cleft. 128–131. Simulium (Anasolen) Enderlein, 1930. 128. ambositrae Grenier & Grjebine, 1959. 129. dentulosum Roubaud, 1915. 130. imerinae Roubaud, 1905. 131. nili Gibbins, 1934. — 132–135. S. (Freemanellum) Crosskey, 1969. 132. berghei Fain, 1949. 133. hirsutilateris De-Meillon, 1937. 134. debegene De-Meillon, 1934. 135. manense Elsen & Escaffre, 1976. — 136–139. S. (Hearlea) Vargas et al., 1946. 136. ayrozai Vargas, 1945. 137. canadense Hearle, 1932. 138. capricorne De León, 1945. 139. larvispinosum De León, 1948. — 140–143. S. (Hemicnetha) Enderlein, 1934. 140. bricenoi Vargas et al., 1946. 141. cristalinum Coscarón & Py-Daniel, 1989. 142. paynei Vargas, 1942. 143. rubrithorax Lutz, 1909. — 144. S. (Obuchovia) galloprovinciale Giudicelli, 1963. — 145–147. S. (Trichodagmia) Enderlein, 1934. 145. hirtipupa Lutz, 1910. 146. lahillei (Paterson & Shannon, 1927). 147. nigrimanum Macquart, 1838. — 148–149. S. (Disculter) subgen. nov. 148. oviedoi Ramírez-Pérez, 1971. 149. rivasi Ramírez-Pérez, 1971. Scale bars = 0.2 mm.
Figs 91–106 in Simulium (Trichodagmia) (Diptera, Simuliidae) phylogeny revisited: the Neotropical and Afrotropical connection
Figs 91–106. Gills of pupae. 91–94. Simulium (Anasolen) Enderlein, 1930. 91. bisnovem Gibbins, 1938. 92. dentulosum Roubaud, 1915. 93. imerinae Roubaud, 1905. 94. masabae Gibbins, 1934. — 95– 97. S. (Freemanellum) Crosskey, 1969. 95. debegene De-Meillon, 1934. 96. manense Elsen & Escaffre, 1976. 97. hessei Gibbins, 1941. — 98. S. (Hearlea) canadense Hearle, 1932. — 99–102. S. (Hemicnetha) Enderlein, 1934. 99. cristalinum Coscarón & Py-Daniel, 1989. 100. earlei Vargas et al., 1946. 101. paynei Vargas, 1942. 102. virgatum Coquillett, 1902. —103. S. (Obuchovia) galloprovinciale Giudicelli, 1963. — 104–106. S. (Trichodagmia) Enderlein, 1934. 104. nigrimanum Macquart, 1838. 105. hirtipupa Lutz, 1910. 106. scutistriatum Lutz, 1909. Scale bars: 91–104, 106 = 0.2 mm; 105 = 0.05 mm.
Figs 50–70. Males. Gonocoxite and gonostyle. 50–54 in Simulium (Trichodagmia) (Diptera, Simuliidae) phylogeny revisited: the Neotropical and Afrotropical connection
Figs 50–70. Males. Gonocoxite and gonostyle. 50–54. Simulium (Anasolen) Enderlein, 1930. 50. dentulosum Roubaud, 1915. 51. imerinae Roubaud, 1905. 52. kauntzeum Gibbins, 1938. 53. masabae Gibbins, 1934. 54. nili Gibbins, 1934. — 55–56. S. (Freemanellum) Crosskey, 1969. 55. hirsutilateris De-Meillon, 1937. 56. manense Elsen & Escaffre, 1976. — 57–59. S. (Hearlea) Vargas et al. 1946. 57. ayrozai Vargas, 1945. 58. canadense Hearle, 1932. 59. capricorne De León, 1945. — 60–62. S. (Hemicnetha) Enderlein, 1934. 60. brachycladum Lutz & Pinto, 1932. 61. cristalinum Coscarón & Py-Daniel, 1989. 62. tarsatum Macquart, 1846. — 63. S. (Shewellomyia) claricentrum Adler, 1990. — 64–68. S. (Trichodagmia) Enderlein, 1934. 64. guianense Wise, 1911. 65. hirtipupa Lutz, 1910. 66. itaunense D'Andretta & Dolores González, 1964. 67. lahillei (Paterson & Shannon, 1927). 68. nigrimanum Macquart, 1838. — 69–70. S. (Disculter) subgen. nov. 69. rivasi Ramírez-Pérez, 1971. 70. oviedoi Ramírez-Pérez, 1971. Scale bars = 0.1 mm.
Figs 33–49. Males. Ventral plate. 33–37 in Simulium (Trichodagmia) (Diptera, Simuliidae) phylogeny revisited: the Neotropical and Afrotropical connection
Figs 33–49. Males. Ventral plate. 33–37. Simulium (Anasolen) Enderlein, 1930. 33. dentulosum Roubaud, 1915. 34. imerinae Roubaud, 1905. 35. kauntzeum Gibbins, 1938. 36. masabae Gibbins, 1934. 37. nili Gibbins, 1934. — 38. S. (Freemanellum) debegene De-Meillon, 1934. — 39– 40. S. (Hearlea) Vargas et al. 1946. 39. ayrozai Vargas, 1945. 40. larvispinosum De León, 1948. — 41–42. S. (Hemicnetha) Enderlein, 1934. 41. bricenoi Vargas et al., 1946. 42. tarsatum Macquart, 1846. — 43. S. (Shewellomyia) claricentrum Adler, 1990. — 44. S. (Obuchovia) galloprovinciale Giudicelli, 1963. — 45–47. S. (Trichodagmia) Enderlein, 1934. 45. itaunense D'Andretta & Dolores González, 1964. 46. lahillei (Paterson & Shannon, 1927). 47. scutistriatum Lutz, 1909. — 48–49. S. (Disculter) subgen. nov. 48. rivasi Ramírez-Pérez, 1971. 49. oviedoi Ramírez-Pérez, 1971. Scale bars = 0.1 mm.
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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.