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431 results for “areas of endemism”

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zenodo32/100

FIGURE 5 in Effect of cell size and thresholds in NDM/NVDM methods on recognizing areas of endemism

FIGURE 5. Consensus areas supported by taxa with non-sympatric distribution, cell size 1° x 1° cell. The different letter indicates the species' ei minimum value that supports the areas of endemism in each analysis. A: no definition of ei minimum, B: ei minimum = 1, C: ei minimum = 0.9, D: ei minimum = 0.8, E: ei minimum = 0.7 and F: ei minimum = 0. On each map, we display the corresponding final area number. For the list of taxa that support each area, see Table S3.

opennotspecifiedMay 2022View details →
zenodo32/100

FIGURE 6 in Effect of cell size and thresholds in NDM/NVDM methods on recognizing areas of endemism

FIGURE 6. Consensus areas supported by taxa with non-sympatric distribution, cell size 0.5°x0.5° cell. The different letter indicates the species' minimum ei value that supports the areas of endemism in each analysis. A: no definition of ei minimum, B: ei minimum = 1, C: ei minimum = 0.9, D: ei minimum = 0.8, E: ei minimum = 0.7 and F: ei minimum = 0. On each map, we display the corresponding final area number. For the list of taxa that support each area, see Table S3.

opennotspecifiedMay 2022View details →
zenodo32/100

FIGURE 4 in Effect of cell size and thresholds in NDM/NVDM methods on recognizing areas of endemism

FIGURE 4. Final endemism areas resulted from the six analyses varying the minimum ei with 0.25 ° x 0.25 ° cells. The different letter indicates the species' minimum value that supports the areas in each run. A: no definition of ei minimum, B: ei minimum = 1, C: ei minimum = 0.9, D: ei minimum = 0.8, E: ei minimum = 0.7 and F: ei minimum = 0. On each map, we display the corresponding final area number. For the list of taxa that support each area, see Table S1.

opennotspecifiedMay 2022View details →
zenodo32/100

Distribution. Endemic to West Java Province, Indonesia, known only from two localities, Cibadak and Cibodas, in the Bogor area just S ofJakarta. in Molossidae

Distribution. Endemic to West Java Province, Indonesia, known only from two localities, Cibadak and Cibodas, in the Bogor area just S ofJakarta.

opennotspecifiedOct 2019View details →
zenodo32/100

Distribution. Endemic to subtropical and tropical waters of the Atlantic Ocean in an area ranging from N USA to Brazil and from Ireland to Guinea-Bissau; its distribution may continue as far S as Uruguay in the W, and possibly as far S as Angola in the E. It is occasionally recorded stranding in temperate waters, but these may represent vagrant individuals. in Ziphiidae

Distribution. Endemic to subtropical and tropical waters of the Atlantic Ocean in an area ranging from N USA to Brazil and from Ireland to Guinea-Bissau; its distribution may continue as far S as Uruguay in the W, and possibly as far S as Angola in the E. It is occasionally recorded stranding in temperate waters, but these may represent vagrant individuals.

opennotspecifiedJul 2014View details →
zenodo32/100

Distribution. Endemic to Tanzania, known only from six small remnant moist-forest patches in C coastal and extreme SE Tanzania (Litipo, Rondo, Ziwani, Pugu Hills/ Kazimzumbwi, and Zareninge), and the Pande Game Reserve; it is not known if it occurs in the intervening areas. in Galagidae

Distribution. Endemic to Tanzania, known only from six small remnant moist-forest patches in C coastal and extreme SE Tanzania (Litipo, Rondo, Ziwani, Pugu Hills/ Kazimzumbwi, and Zareninge), and the Pande Game Reserve; it is not known if it occurs in the intervening areas.

opennotspecifiedMar 2013View details →
zenodo32/100

Distribution. Known only from the Konteh Area of the Sanetti Plateau in SC Ethiopia; it remains possible that this recently described species inhabits other parts of the plateau as well, although it is likely endemic to the Bale Mts. in Soricidae

Distribution. Known only from the Konteh Area of the Sanetti Plateau in SC Ethiopia; it remains possible that this recently described species inhabits other parts of the plateau as well, although it is likely endemic to the Bale Mts.

opennotspecifiedJul 2018View details →
zenodo32/100

Distribution. Endemic to C & SE Sulawesi; known from various lowland and more mountainous regions, including Mt Rorekatimbo, Mt Gandangdewata, Mt Balease, and Mt Nokilalaki. Together with the Elongated White-toothed Shrew (C. elongata) this is the only wild shrew occurring on the SE peninsula, but lack of adequate sampling in most pristine areas of S Sulawesi hinders precise biogeographical inferences. in Soricidae

Distribution. Endemic to C & SE Sulawesi; known from various lowland and more mountainous regions, including Mt Rorekatimbo, Mt Gandangdewata, Mt Balease, and Mt Nokilalaki. Together with the Elongated White-toothed Shrew (C. elongata) this is the only wild shrew occurring on the SE peninsula, but lack of adequate sampling in most pristine areas of S Sulawesi hinders precise biogeographical inferences.

opennotspecifiedJul 2018View details →
zenodo32/100

Imunnesenescence of antibody repertoire in individuals from endemic areas for infectious diseases

<p>Heavy Chain Antibody Repertoire data in the AIRR format, clonotyped with YClon, of patients diagnosed with COVID-19 and a control group. The sample labels in the paper and the sample labels in this repository are correspondent according to the following table:</p> <table> <tbody> <tr> <td>Sample</td> <td>Deposite_code</td> </tr> <tr> <td>C_01</td> <td>A04</td> </tr> <tr> <td>C_02</td> <td>A20</td> </tr> <tr> <td>C_03</td> <td>A24</td> </tr> <tr> <td>C_04</td> <td>A65</td> </tr> <tr> <td>C_05</td> <td>A66</td> </tr> <tr> <td>C_06</td> <td>A67</td> </tr> <tr> <td>H_NEA_01</td> <td>ID141</td> </tr> <tr> <td>H_NEA_02</td> <td>ID143</td> </tr> <tr> <td>H_NEA_03</td> <td>ID144</td> </tr> <tr> <td>H_NEA_04</td> <td>ID187</td> </tr> <tr> <td>H_NEA_05</td> <td>ID195</td> </tr> <tr> <td>H_NEA_06</td> <td>ID226</td> </tr> <tr> <td>H_NEA_07</td> <td>ID248</td> </tr> <tr> <td>H_NEA_08</td> <td>ID268</td> </tr> <tr> <td>H_NEA_09</td> <td>ID310</td> </tr> <tr> <td>H_NEA_10</td> <td>ID375</td> </tr> <tr> <td>M_EA_01</td> <td>GV43</td> </tr> <tr> <td>M_EA_02</td> <td>GV68</td> </tr> <tr> <td>M_EA_03</td> <td>GV106</td> </tr> <tr> <td>M_EA_04</td> <td>GV144</td> </tr> <tr> <td>M_EA_05</td> <td>GV146</td> </tr> <tr> <td>M_EA_06</td> <td>GV47</td> </tr> <tr> <td>M_EA_07</td> <td>GV50</td> </tr> <tr> <td>M_EA_08</td> <td>GV51</td> </tr> <tr> <td>M_EA_09</td> <td>GV54</td> </tr> <tr> <td>M_EA_10</td> <td>GV92</td> </tr> <tr> <td>M_NEA_01</td> <td>ID094</td> </tr> <tr> <td>M_NEA_02</td> <td>ID117</td> </tr> <tr> <td>M_NEA_03</td> <td>ID124</td> </tr> <tr> <td>M_NEA_04</td> <td>ID131</td> </tr> <tr> <td>M_NEA_05</td> <td>ID132</td> </tr> <tr> <td>M_NEA_06</td> <td>ID155</td> </tr> <tr> <td>M_NEA_07</td> <td>ID240</td> </tr> <tr> <td>M_NEA_08</td> <td>ID244</td> </tr> </tbody> </table>

opencc-by-4.0Jul 2024View details →
zenodo32/100

FIGURE 6 in Primary hypotheses of global areas of endemism based on the distribution of Tabanomorpha (Diptera, Brachycera)

FIGURE 6. Areas of endemism recovered in the Oriental and Australian regions by the consensus of the endemicity analysis of Tabanomorpha.

opennotspecifiedMar 2018View details →
zenodo32/100

FIGURE 5 in Primary hypotheses of global areas of endemism based on the distribution of Tabanomorpha (Diptera, Brachycera)

FIGURE 5. Areas of endemism recovered in the African and European regions bY the consensus of the endemicitY analYsis of Tabanomorpha.

opennotspecifiedMar 2018View details →
zenodo32/100

FIGURE 4 in Primary hypotheses of global areas of endemism based on the distribution of Tabanomorpha (Diptera, Brachycera)

FIGURE 4. Areas of endemism recovered in the Nearctic region bY the consensus of the endemicitY analYsis of Tabanomorpha.

opennotspecifiedMar 2018View details →
zenodo32/100

FIGURE 2 in Primary hypotheses of global areas of endemism based on the distribution of Tabanomorpha (Diptera, Brachycera)

FIGURE 2. Relationship among relative number of consensus areas and increasing consensus cut-off values (10% to 100%) in each grid siZe. Also shoWn is the curve fitted for a grid siZe of 7° data. The black dot in the curve corresponds to 31%, the percentage of similaritY of species used to calculate the consensus areas.

opennotspecifiedMar 2018View details →
zenodo32/100

FIGURE 3 in Primary hypotheses of global areas of endemism based on the distribution of Tabanomorpha (Diptera, Brachycera)

FIGURE 3. The area of endemism recovered in the Neotropical region bY the consensus of the endemicitY analYsis of Tabanomorpha did not distinguish the regions Within Neotropics.

opennotspecifiedMar 2018View details →
zenodo32/100

FIGURE 1 in Primary hypotheses of global areas of endemism based on the distribution of Tabanomorpha (Diptera, Brachycera)

FIGURE 1. Logistic curve for the exponential groWth rate of the relative number of areas against their respective grid siZe. The saturation point is the value corresponding to less than 5% of the maximum asYmptote.

opennotspecifiedMar 2018View details →
zenodo32/100

FIGURE 3 in Three new species of Holoscolex (Clitellata, Glossoscolecidae) from the Gurupi Biological Reserve, last forest remnant of the Belém Endemism Area, Eastern Amazon

FIGURE 3. Holoscolex alatus sp. nov. (holotype). A. Ventral view of anterior region. B. Common seta on right A line of XXX. C. Genital seta on right A line of XXII. D. Dorsal view of right calciferous glands. G, glandular region; M, membranous region. E. Frontal view of left post-clitellar nephridium. np, nephropore; npt, nephrostome; V, nepridium vesicle; Nm, Nematoda; Bd, bladder. F. Dorsal view of right spermatheca of VIII.

opennotspecifiedOct 2018View details →
zenodo32/100

FIGURE 5 in Three new species of Holoscolex (Clitellata, Glossoscolecidae) from the Gurupi Biological Reserve, last forest remnant of the Belém Endemism Area, Eastern Amazon

FIGURE 5. Different arrangements of atrial glands of Holoscolex fernandoi, schematic. AG, atrial glands.

opennotspecifiedOct 2018View details →
zenodo32/100

FIGURE 1 in Three new species of Holoscolex (Clitellata, Glossoscolecidae) from the Gurupi Biological Reserve, last forest remnant of the Belém Endemism Area, Eastern Amazon

FIGURE 1. Localization of sampling site within Belém Endemism Area and Gurupi Biological Reserve in Maranhão state, Brazil.

opennotspecifiedOct 2018View details →
zenodo32/100

FIGURE 4 in Three new species of Holoscolex (Clitellata, Glossoscolecidae) from the Gurupi Biological Reserve, last forest remnant of the Belém Endemism Area, Eastern Amazon

FIGURE 4. Holoscolex fernandoi sp. nov. (holotype). A. Latero-ventral view of anterior region. a, A setae; b, B setae; c, C setae. B. Genital seta of papillae on right A line of XX. C. Common seta on right A line of XXX. D. Dorsal view of right calciferous gland. BV, blood vessel; G, glandular region; M, membranous region. E. Dorsal view of right spermathecae of VII and VIII. F. Lateral view of left post-clitellar nephidium. np, nephropore; npt, nephrostome; V, nepridium vesicle; Bd, bladder. G. Dorsal view of a left common atrial gland of XIX.

opennotspecifiedOct 2018View details →
zenodo32/100

FIGURE 2 in Three new species of Holoscolex (Clitellata, Glossoscolecidae) from the Gurupi Biological Reserve, last forest remnant of the Belém Endemism Area, Eastern Amazon

FIGURE 2. Holoscolex dossantosi sp. nov. (holotype). A. Ventral view of clitellar region. B. Genital setae of right papilla on A line of XVIII. C. Common seta of right A line of XXX. D. Dorsal view of right calciferous gland. BV, blood vessel; G, glandular region; M, membranous region. E. Frontal view of right post-clitellar nephridium. np, nephropore; npt, nephrostome; V, nepridium vesicle; Bd, bladder. F. Dorsal view of right spermatheca of VIII.

opennotspecifiedOct 2018View details →

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