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Distribution. Two disjunct areas across the lowland rainforest belt of W Africa (Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo & Benin) and C Africa through the Congo Basin (Cameroon, Gabon, Republic of the Congo, DR Congo, Central African Republic & extreme SW Sudan), and five very small disjunct populations in mountainous areas in C Kenya. in Bovidae
Distribution. Two disjunct areas across the lowland rainforest belt of W Africa (Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo & Benin) and C Africa through the Congo Basin (Cameroon, Gabon, Republic of the Congo, DR Congo, Central African Republic & extreme SW Sudan), and five very small disjunct populations in mountainous areas in C Kenya.
Distribution. NW Colombia, between the Rio Atrato and the lower Rio Cauca (W of the Rio Cauca and the Mompos I) and Rio Magdalena (from the Uraba region, W of the Rio Cauca), and NE Choco Department, E of the Rio Atrato, from sea level to ¢.400 m. Small, introduced populations occur in Tayrona National Natural Park (15,000 ha) and on some small Is near Cartagena and in Panama, outside its natural distribution. in Callitrichiade
Distribution. NW Colombia, between the Rio Atrato and the lower Rio Cauca (W of the Rio Cauca and the Mompos I) and Rio Magdalena (from the Uraba region, W of the Rio Cauca), and NE Choco Department, E of the Rio Atrato, from sea level to ¢.400 m. Small, introduced populations occur in Tayrona National Natural Park (15,000 ha) and on some small Is near Cartagena and in Panama, outside its natural distribution.
Distribution. Sub-Saharan Africa; virtually eradicated from W Africa, and greatly reduced in C and NE Africa. The largest populations exist in Botswana, Tanzania, and Zimbabwe, which account for approximately half of the estimated number of African Wild Dogs remaining in the wild. Other populations occur in Central African Republic, Ethiopia, Kenya, Mozambique, Namibia, South Africa, Sudan, and Zambia. Potential small populations (less than 100 individuals) may exist in Cameroon, Chad, Senegal, and Somalia. in Canidae
Distribution. Sub-Saharan Africa; virtually eradicated from W Africa, and greatly reduced in C and NE Africa. The largest populations exist in Botswana, Tanzania, and Zimbabwe, which account for approximately half of the estimated number of African Wild Dogs remaining in the wild. Other populations occur in Central African Republic, Ethiopia, Kenya, Mozambique, Namibia, South Africa, Sudan, and Zambia. Potential small populations (less than 100 individuals) may exist in Cameroon, Chad, Senegal, and Somalia.
Distribution. Two disjunct areas across the lowland rainforest belt of W Africa (Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo & Benin) and C Africa through the Congo Basin (Cameroon, Gabon, Republic of the Congo, DR Congo, Central African Republic & extreme SW Sudan), and five very small disjunct populations in mountainous areas in C Kenya. in Bovidae
Distribution. Two disjunct areas across the lowland rainforest belt of W Africa (Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo & Benin) and C Africa through the Congo Basin (Cameroon, Gabon, Republic of the Congo, DR Congo, Central African Republic & extreme SW Sudan), and five very small disjunct populations in mountainous areas in C Kenya.
Subspecies and Distribution. L.v.victoriaeThomas,1893—Tanzania. L.v.angolensisThomas,1904—Angola. L.v.senegalensisRochebrune,1883—Senegal,TheGambia. L. v. whyte: Thomas, 1894 — Malawi. The African Savanna Hare is present from the Atlantic coast of NW Africa (Western Sahara S to Guinea), E across the Sahel to Sudan and the extreme W Ethiopia, S through E Africa (E DR Congo, Uganda, W Kenya, Rwanda, Burundi, and Tanzania) to most of Angola, Zambia, Malawi, NE Namibia, Botswana, Zimbabwe, Mozambique, E South Africa, Swaziland, and Lesotho; a small isolated population exists near Beni Abbas in the Sahara Desert in W Algeria. in Leporidae
Subspecies and Distribution. L.v.victoriaeThomas,1893—Tanzania. L.v.angolensisThomas,1904—Angola. L.v.senegalensisRochebrune,1883—Senegal,TheGambia. L. v. whyte: Thomas, 1894 — Malawi. The African Savanna Hare is present from the Atlantic coast of NW Africa (Western Sahara S to Guinea), E across the Sahel to Sudan and the extreme W Ethiopia, S through E Africa (E DR Congo, Uganda, W Kenya, Rwanda, Burundi, and Tanzania) to most of Angola, Zambia, Malawi, NE Namibia, Botswana, Zimbabwe, Mozambique, E South Africa, Swaziland, and Lesotho; a small isolated population exists near Beni Abbas in the Sahara Desert in W Algeria.
Distribution. NW Madagascar from the Mahavavy River S to the Andranomalaza River, the E limit is poorly defined, butlikely occurs at the Tsaratanana Massif, and there are additional populations in forests of the Ampasindava Peninsula, on the inshore islands of Nosy Be and Nosy Komba, and in the coastal forests NE of Ambanja (including the peninsula leading to Nosy Faly). Introduced into the small islet of Nosy Tanikely. in Lemuridae
Distribution. NW Madagascar from the Mahavavy River S to the Andranomalaza River, the E limit is poorly defined, butlikely occurs at the Tsaratanana Massif, and there are additional populations in forests of the Ampasindava Peninsula, on the inshore islands of Nosy Be and Nosy Komba, and in the coastal forests NE of Ambanja (including the peninsula leading to Nosy Faly). Introduced into the small islet of Nosy Tanikely.
Distribution. SE Madagascar in a thin strip of forest from just above the Manampatrana River S to the Mananara River, with a small isolated population at Manombo and Agnalazaha on the coast S of Farafangana. in Lemuridae
Distribution. SE Madagascar in a thin strip of forest from just above the Manampatrana River S to the Mananara River, with a small isolated population at Manombo and Agnalazaha on the coast S of Farafangana.
Distribution. NE Australia, a small population persists at Epping Forest National Park near Clermont in C Queensland. in Vombatidae
Distribution. NE Australia, a small population persists at Epping Forest National Park near Clermont in C Queensland.
Distribution. Japan, mainly E Honshu and adjacent islands, as well as isolated populations in W Japan, including W Honshu (Hiwa Town, Kyoto City, and Kii Peninsula), Shikoku (Mt Ishizuchi, Mt Tsurugi, and Mt Ohtaki), and Shodoshima I; W limit of distribution on E Honshu is located across Ishikawa, Gifu, Nagano, and Shizuoka prefectures, where SmallJapanese Mole shows parapatric or mixed distribution with the Large Japanese Mole (M. wogura), a species distributed in W Japan. In Echigo Plain, Niigata Prefecture, the Small Japanese Mole is parapatric with the Echigo Mole (M. etigo). in Talpidae
Distribution. Japan, mainly E Honshu and adjacent islands, as well as isolated populations in W Japan, including W Honshu (Hiwa Town, Kyoto City, and Kii Peninsula), Shikoku (Mt Ishizuchi, Mt Tsurugi, and Mt Ohtaki), and Shodoshima I; W limit of distribution on E Honshu is located across Ishikawa, Gifu, Nagano, and Shizuoka prefectures, where SmallJapanese Mole shows parapatric or mixed distribution with the Large Japanese Mole (M. wogura), a species distributed in W Japan. In Echigo Plain, Niigata Prefecture, the Small Japanese Mole is parapatric with the Echigo Mole (M. etigo).
Subspecies and Distribution. N. ¢c. concolor Harlan, 1826 — S China (C & SW Yunnan Province) including a small population W of the Mekong River near the Myanmar border, and N Vietnam (Lao Cai, Son La, and Yen Bai provinces) between the Black and Red rivers from ¢.20° N 023° 45° N. c. c. lu Delacour, 1951 — NW Laos (Bokeo and Luang Namtha provinces) in an isolated population E of the Mekong River at ¢.20° 17° N-20° 25' N. in Hylobatidae
Subspecies and Distribution. N. ¢c. concolor Harlan, 1826 — S China (C & SW Yunnan Province) including a small population W of the Mekong River near the Myanmar border, and N Vietnam (Lao Cai, Son La, and Yen Bai provinces) between the Black and Red rivers from ¢.20° N 023° 45° N. c. c. lu Delacour, 1951 — NW Laos (Bokeo and Luang Namtha provinces) in an isolated population E of the Mekong River at ¢.20° 17° N-20° 25' N.
Distribution. Java, mainly in W provinces (Banten and West Java), with an additional population in a small area in the C as far E as the Dieng Mts. in Hylobatidae
Distribution. Java, mainly in W provinces (Banten and West Java), with an additional population in a small area in the C as far E as the Dieng Mts.
Distribution. Patchily distributed on E side of Great Dividing Range from N of Brisbane, Queensland, to Kangaroo Valley, New South Wales. Small isolated populations persist W of the Great Dividing Range in N New South Wales (in the Warrumbungles and at Mt Kaputar) and in E Victoria (East Gippsland). in Macropodidae
Distribution. Patchily distributed on E side of Great Dividing Range from N of Brisbane, Queensland, to Kangaroo Valley, New South Wales. Small isolated populations persist W of the Great Dividing Range in N New South Wales (in the Warrumbungles and at Mt Kaputar) and in E Victoria (East Gippsland).
Data from: Population variation reveals independent selection towards small body size in Chinese Debao pony
Body size, one of the most important quantitative traits under evolutionary scrutiny, varies considerably among species and among populations within species. Revealing the genetic basis underlying this variation is very important, particularly in humans where there is a close relationship with diseases and in domestic animals as the selective patterns are associated with improvements in production traits. The Debao pony is a horse breed with small body size that is unique to China; however, it is unknown whether the size-related candidate genes identified in Western breeds also account for the small body size of the Debao pony. Here, we compared individual horses from the Debao population with other two Chinese horse populations using SNPs identified with the Equine SNP 65 Bead Chip. The previously reported size-related candidate gene HMGA2 showed a significant signature for selection, consistent with its role observed in human populations. More interestingly, we found a candidate gene TBX3, which had not been observed in previous studies on horse body size that displayed the highest differentiation and most significant association, and thus likely is the dominating factor for the small stature of the Debao pony. Further comparison between the Debao pony and other breeds of horses from around the world demonstrated that TBX3 was selected independently in the Debao pony, suggesting that there were multiple origins of small stature in the horse.
Distribution. Northern Iberian Peninsula, discontinuously from Galicia and N Portugal (N of upper Mondego River) E to both sides of the Pyrenees, also in W Central System and N Iberian System Mts; two small isolated populations in Zézere River (Portugal) and Mayor River (Vizcaya, Spain). in Talpidae
Distribution. Northern Iberian Peninsula, discontinuously from Galicia and N Portugal (N of upper Mondego River) E to both sides of the Pyrenees, also in W Central System and N Iberian System Mts; two small isolated populations in Zézere River (Portugal) and Mayor River (Vizcaya, Spain).
Subspecies and Distribution. S.a.anomalusGmelin,1778—Lesbos1(Greece),Turkey,Georgia,Armenia,Azerbaijan,andperhapsNIraq. S.a.pallescensGray,1867—NIraq,andW&SIran(ZagrosMtsandFarsDistrict). S. a. syriacus Ehrenberg, 1828 — Lebanon, W Syria, N Israel, and a small isolated population in extreme NWJordan. in Sciuridae
Subspecies and Distribution. S.a.anomalusGmelin,1778—Lesbos1(Greece),Turkey,Georgia,Armenia,Azerbaijan,andperhapsNIraq. S.a.pallescensGray,1867—NIraq,andW&SIran(ZagrosMtsandFarsDistrict). S. a. syriacus Ehrenberg, 1828 — Lebanon, W Syria, N Israel, and a small isolated population in extreme NWJordan.
Distribution. SE Nigeria, in a few small, scattered populations in forest and derived savanna between the lower Niger and Cross rivers, including the Niger Delta (specifically, from W of Oguta at 5° 42° N, just E of the Niger); it occurs N as far as the Eastern Aboine River in Ebonyi State. in Cercopithecidae
Distribution. SE Nigeria, in a few small, scattered populations in forest and derived savanna between the lower Niger and Cross rivers, including the Niger Delta (specifically, from W of Oguta at 5° 42° N, just E of the Niger); it occurs N as far as the Eastern Aboine River in Ebonyi State.
Distribution. SE Kenya, endemic to riparian forest patches along the lower Tana River; an additional small population was recently discovered in the Tana River Delta. in Cercopithecidae
Distribution. SE Kenya, endemic to riparian forest patches along the lower Tana River; an additional small population was recently discovered in the Tana River Delta.
Nesokia is sister to Bandicota and are nested in Rattus phylogenetically, making Rat- tus paraphyletic. Tarsomys, Limnomys, and Diplothrix are also phylogenetically in Rat- tus, and the clade is in need of focused re- vision at the generic level. Nesokia bunnui was originally described as a separate ge-nus, Erythronesokia, because it is morphologically very distinctive from N. indica. Type specimen was destroyed during the Iraq War, and a neotype was recently designated to replace it. Monotypic. Distribution. Tigris and Euphrates river valleys, SE Iraq. Descriptive notes. Head—body 230-260 mm, tail 205-270 mm, ear 18-21 mm, hindfoot 49-58 mm; weight 519 g. The Long-tailed Bandicoot Rat is larger than the Short-tailed Bandicoot Rat (N. indica). Pelage is soft and woolly, interspersed with harsher coarse hair and long black hairs near mid-back. Dorsum is fawn to ocherous red, washed with purple or chestnuton darker individuals. Hairs are basally slate-gray and distally rufous, occasionally with whitish or black tips. Muzzle is drab. Sides arefawn, with gray edge toward venter. Venteris whitish, extending onto cheeks where the same pattern from gray to fawn to dorsal pelage occurs. Feet are large and robust, being light brown and well-furred dorsally. Claws are amber on forefeet and dull brown on hindfeet; pollux is extremely small. Ears are moderately long and brownish, with no hair internally. Tail is ¢.82-104% of head-body length and deep brownish drab, interspersed with visible white hair. Skull is large and robust, similarly to the Short-tailed Bandicoot Rat. Habitat. Marsh and swamp land. Food and Feeding. No information. Breeding. No information. Activity patterns. The Long-tailed Bandicoot Rat is terrestrial, although it isfound in swampy and marshy areas and is probably amphibious. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List. The Longtailed Bandicoot Rat is apparently rare and is known from very few specimens. Marsh and swamp habitats in which it is found were completely destroyed during the Iraq War by draining, war damage, and agricultural expansion. In recent years, flooding from Tigris and Euphrates rivers and high snow fall and melt haveresulted in partial restoration ofits native habitat, although restoration is not a complete. Populations are now probably highly fragmented. Bibliography. Al-Ansari et al. (2012), Al-Robaae & Felten (1990), Khajuria (1981), Krystufek et al. (2017), Musser & Carleton (2005), Richardson & Hussain (2006), Stuart (2008). in Muridae
Nesokia is sister to Bandicota and are nested in Rattus phylogenetically, making Rat- tus paraphyletic. Tarsomys, Limnomys, and Diplothrix are also phylogenetically in Rat- tus, and the clade is in need of focused re- vision at the generic level. Nesokia bunnui was originally described as a separate ge-nus, Erythronesokia, because it is morphologically very distinctive from N. indica. Type specimen was destroyed during the Iraq War, and a neotype was recently designated to replace it. Monotypic. Distribution. Tigris and Euphrates river valleys, SE Iraq. Descriptive notes. Head—body 230-260 mm, tail 205-270 mm, ear 18-21 mm, hindfoot 49-58 mm; weight 519 g. The Long-tailed Bandicoot Rat is larger than the Short-tailed Bandicoot Rat (N. indica). Pelage is soft and woolly, interspersed with harsher coarse hair and long black hairs near mid-back. Dorsum is fawn to ocherous red, washed with purple or chestnuton darker individuals. Hairs are basally slate-gray and distally rufous, occasionally with whitish or black tips. Muzzle is drab. Sides arefawn, with gray edge toward venter. Venteris whitish, extending onto cheeks where the same pattern from gray to fawn to dorsal pelage occurs. Feet are large and robust, being light brown and well-furred dorsally. Claws are amber on forefeet and dull brown on hindfeet; pollux is extremely small. Ears are moderately long and brownish, with no hair internally. Tail is ¢.82-104% of head-body length and deep brownish drab, interspersed with visible white hair. Skull is large and robust, similarly to the Short-tailed Bandicoot Rat. Habitat. Marsh and swamp land. Food and Feeding. No information. Breeding. No information. Activity patterns. The Long-tailed Bandicoot Rat is terrestrial, although it isfound in swampy and marshy areas and is probably amphibious. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List. The Longtailed Bandicoot Rat is apparently rare and is known from very few specimens. Marsh and swamp habitats in which it is found were completely destroyed during the Iraq War by draining, war damage, and agricultural expansion. In recent years, flooding from Tigris and Euphrates rivers and high snow fall and melt haveresulted in partial restoration ofits native habitat, although restoration is not a complete. Populations are now probably highly fragmented. Bibliography. Al-Ansari et al. (2012), Al-Robaae & Felten (1990), Khajuria (1981), Krystufek et al. (2017), Musser & Carleton (2005), Richardson & Hussain (2006), Stuart (2008).
Distribution. Now restricted to the Channel Country of SW Queensland and the Lake Eyre Basin in NE South Australia. Descriptive notes. Head-body 95-120 mm, tail 105-160 mm, ear 23-29 mm, hindfoot 32-37 mm; weight 30-50 g. The Fawn Hopping Mouse has body form typical of hopping mice, with very long hindfeet, long tail with distal brush of longer hairs, very long ears, and large protruberant eyes. Dorsal fur is of variable color, from pale pinkish fawn to gray; ventral fur white. Unlike most other hopping mice, it has no throat pouch, but males have a glandular area of naked skin on the chest. Habitat. Occurs in low shrublands and tussock grasslands on stony ("gibber") plains and claypans. Shows marked habitat segregation from the Dusky Hopping Mouse (N. fuscus), which is closely associated with sandy substrates. Food and Feeding. The Fawn Hopping Mouse is mostly granivorous, but also eats other plant material (stems, leaves) and occasionally invertebrates. It uses succulent, salt-adapted plants around edges of claypans as a source of water. Breeding. Reproduction is probably largely opportunistic and aseasonal, with high reproductive output from near-continuous breeding after periods of high rainfall; reported littersize is 1-5, most commonly three; gestation period 38-43 days for nonlactating females. Females may mature later than other hopping mice, with reproductive maturity reached at about six months. Activity patterns. Terrestrial and nocturnal. Fawn Hopping Mice shelter during day in burrow systems that are typically simpler and shallower than those of other hopping mice. Movements, Home range and Social organization. Fawn Hopping Mice generally live singly or in small groups; typically uncommon within range, but population density may increase by an order of magnitude following periods of high rainfall. Status and Conservation. Classified as Near Threatened on The IUCN Red List. The Fawn Hopping Mouse has shown marked decline in range (estimated at greater than 50%), and presumably population size, since European settlement of Australia. This is mostlikely due to predation by the introduced house cat and Red Fox (Vulpes vulpes), and to habitat degradation associated with pastoralism. Bibliography. Brazenor (1934), Burbidge et al. (2008), Finlayson (1939), Gould (1853), Jackson & Groves (2015), Murray et al. (1999), Ogilby (1892), Thomas (1921h), Van Dyck & Strahan (2008), Waite (1898), Watts & Aslin (1981), Woinarski et al. (2014), Wood Jones (1925). in Muridae
Distribution. Now restricted to the Channel Country of SW Queensland and the Lake Eyre Basin in NE South Australia. Descriptive notes. Head-body 95-120 mm, tail 105-160 mm, ear 23-29 mm, hindfoot 32-37 mm; weight 30-50 g. The Fawn Hopping Mouse has body form typical of hopping mice, with very long hindfeet, long tail with distal brush of longer hairs, very long ears, and large protruberant eyes. Dorsal fur is of variable color, from pale pinkish fawn to gray; ventral fur white. Unlike most other hopping mice, it has no throat pouch, but males have a glandular area of naked skin on the chest. Habitat. Occurs in low shrublands and tussock grasslands on stony ("gibber") plains and claypans. Shows marked habitat segregation from the Dusky Hopping Mouse (N. fuscus), which is closely associated with sandy substrates. Food and Feeding. The Fawn Hopping Mouse is mostly granivorous, but also eats other plant material (stems, leaves) and occasionally invertebrates. It uses succulent, salt-adapted plants around edges of claypans as a source of water. Breeding. Reproduction is probably largely opportunistic and aseasonal, with high reproductive output from near-continuous breeding after periods of high rainfall; reported littersize is 1-5, most commonly three; gestation period 38-43 days for nonlactating females. Females may mature later than other hopping mice, with reproductive maturity reached at about six months. Activity patterns. Terrestrial and nocturnal. Fawn Hopping Mice shelter during day in burrow systems that are typically simpler and shallower than those of other hopping mice. Movements, Home range and Social organization. Fawn Hopping Mice generally live singly or in small groups; typically uncommon within range, but population density may increase by an order of magnitude following periods of high rainfall. Status and Conservation. Classified as Near Threatened on The IUCN Red List. The Fawn Hopping Mouse has shown marked decline in range (estimated at greater than 50%), and presumably population size, since European settlement of Australia. This is mostlikely due to predation by the introduced house cat and Red Fox (Vulpes vulpes), and to habitat degradation associated with pastoralism. Bibliography. Brazenor (1934), Burbidge et al. (2008), Finlayson (1939), Gould (1853), Jackson & Groves (2015), Murray et al. (1999), Ogilby (1892), Thomas (1921h), Van Dyck & Strahan (2008), Waite (1898), Watts & Aslin (1981), Woinarski et al. (2014), Wood Jones (1925).
The first comprehensive revision of all the species attributed to Melomys led J. I. Menzies in 1996 to resurrect the genus Paramelomys and to redefine its morphologicallimits and species content. Menzies created P. gressitti as a new species belonging to a group displaying morphological similarities and including also P. lorentzii and P. moncktoni. Monotypic Distribution. E New Guinea. Descriptive notes. Head-body 135-162 mm, hindfoot 30-34 mm; no specific data are available for body weight. Gressitt's Mosaic-tailed Rat is a medium-sized Paramelomys with a soft, thick and woolly pelage, a long narrow foot, and a tail with three hairs per scale. It exhibits a medium-sepia dorsal pelage and a gray-buff ventral one. Tail is slightly shorter (99%) than head-body length. The skull has a narrow zygomatic plate. Habitat. Moist tropical mountain forest between 2300 m and 2400 m. Food and Feeding. No information. Breeding. No information. Activity patterns. Gressitt's Mosaic-tailed Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List owing to its small geographic range (less than 3500 km?*) and the destruction ofits habitat by mining and logging activities. The major threat to Gressitt's Mosaic-tailed Rat is ongoing habitat degradation caused by nearby human populations; habitat on Mount Kandy has been destroyed by gold-miners and wood-cutters. Bibliography. Menzies (1996). in Muridae
The first comprehensive revision of all the species attributed to Melomys led J. I. Menzies in 1996 to resurrect the genus Paramelomys and to redefine its morphologicallimits and species content. Menzies created P. gressitti as a new species belonging to a group displaying morphological similarities and including also P. lorentzii and P. moncktoni. Monotypic Distribution. E New Guinea. Descriptive notes. Head-body 135-162 mm, hindfoot 30-34 mm; no specific data are available for body weight. Gressitt's Mosaic-tailed Rat is a medium-sized Paramelomys with a soft, thick and woolly pelage, a long narrow foot, and a tail with three hairs per scale. It exhibits a medium-sepia dorsal pelage and a gray-buff ventral one. Tail is slightly shorter (99%) than head-body length. The skull has a narrow zygomatic plate. Habitat. Moist tropical mountain forest between 2300 m and 2400 m. Food and Feeding. No information. Breeding. No information. Activity patterns. Gressitt's Mosaic-tailed Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List owing to its small geographic range (less than 3500 km?*) and the destruction ofits habitat by mining and logging activities. The major threat to Gressitt's Mosaic-tailed Rat is ongoing habitat degradation caused by nearby human populations; habitat on Mount Kandy has been destroyed by gold-miners and wood-cutters. Bibliography. Menzies (1996).
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