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FIGURES 4–6 in Description of two new species of the genus Baburia Koçak, 1981 (Lepidoptera: Tortricidae: Olethreutinae) from India
FIGURES 4–6. Labial palps (scale bar—0.5 mm), 4. B. tinsukiaensis n. sp. (male holotype), 5. B. tinsukiaensis n. sp. (female paratype), 6. B. chettalliensis n. sp. (male holotype).
FIGURES 11–13. B. tinsukiaensis n in Description of two new species of the genus Baburia Koçak, 1981 (Lepidoptera: Tortricidae: Olethreutinae) from India
FIGURES 11–13. B. tinsukiaensis n. sp. (male holotype), 11. Male genitalia, 12. Uncus, 13. Aedeagus.
AERA5-Asia: A long-term Asian precipitation dataset (0.1°, 1 hourly, 1951–2015, Asia) anchoring the ERA5-Land under the total volume control by APHRODITE (1967–1981)
<p>AERA5-Asia: A long-term Asian precipitation dataset (0.1°, 1 hourly, 1951–2015, Asia) is developed by organically combining the ERA5-Land dataset with high spatiotemporal resolutions and continuity and the APHRODITE dataset with high quality.</p> <p><strong>How to cite: Ma, Z., Xu, J., Ma, Y., Zhu, S., He, K., Zhang, S., Ma, W., Xu, X., 2022. AERA5-Asia: A long-term Asian precipitation dataset (0.1°, 1 hourly, 1951–2015, Asia) anchoring the ERA5-Land under the total volume control by APHRODITE. Bulletin of American Meteorological Society, 103 (4)., DOI: https://doi.org/10.1175/BAMS-D-20-0328.1.</strong></p> <p>Data Format: GeoTIFF</p> <p>Spatial Coverage: 60°E–150°E, 15°S–55°N, land.</p> <p>AERA5-Asia (0.1°/ hourly, 1951–1966, Asia) is available at <a href="https://doi.org/10.5281/zenodo.3609352">https://doi.org/</a><a href="https://doi.org/10.5281/zenodo.4266081">10.5281/zenodo.6367463</a></p> <p>AERA5-Asia (0.1°/ hourly, 1982–1998, Asia) is available at <a href="https://doi.org/10.5281/zenodo.3609352">https://doi.org/</a><a href="https://doi.org/10.5281/zenodo.4266081">10.5281/zenodo.4266081</a></p> <p>AERA5-Asia (0.1°/ hourly, 1999–2015, Asia) is available at <a href="https://doi.org/10.5281/zenodo.3609352">https://doi.org/</a><a href="https://doi.org/10.5281/zenodo.4264451">10.5281/zenodo.4264451</a></p>
Subspecies and Distribution. M. t. tristis Waterhouse, 1845 — the Philippines including Palawan I. M. 1. celebensis Peterson, 1981 — Sulawesi and nearby Sanana, Togian, and ButonIs. M. t. grandis Peterson, 1981 — W New Guinea E to Chimbu Province in C Papua New Guina, including Waigeo, Supiori, Biak, and Yapen Is, and Louisiade Archipelago. M. t. insularis Peterson, 1981 — Admiralty Is, Bismarck Archipelago, Solomon Is, and Vanuatu (Espirito Santo and Efate Is). M. t. propitristis Peterson, 1981 — E New Guinea. in Miniopteridae
Subspecies and Distribution. M. t. tristis Waterhouse, 1845 — the Philippines including Palawan I. M. 1. celebensis Peterson, 1981 — Sulawesi and nearby Sanana, Togian, and ButonIs. M. t. grandis Peterson, 1981 — W New Guinea E to Chimbu Province in C Papua New Guina, including Waigeo, Supiori, Biak, and Yapen Is, and Louisiade Archipelago. M. t. insularis Peterson, 1981 — Admiralty Is, Bismarck Archipelago, Solomon Is, and Vanuatu (Espirito Santo and Efate Is). M. t. propitristis Peterson, 1981 — E New Guinea.
FIGURES 100–105. Pseudosmittia digitata Saether, 1981, male. 100 in Neotropical Allocladius Kieffer, 1913 and Pseudosmittia Edwards, 1932 (Diptera: Chironomidae) 2472
FIGURES 100–105. Pseudosmittia digitata Saether, 1981, male. 100—tentorium, stipes, and cibarial pump; 101—palp; 102—thorax; 103—wing; 104—hypopygium, dorsal aspect; 105—hypopygium with anal point and tergite IX removed, dorsal aspect to the left, ventral aspect to the right.
Subspecies and Distribution. G.p.personatusTrue,1889—MustangandPadreIs,KlebergCounty,Texas,USA. G.p.davisiWilliams&Genoways,1981—STexas,USA(NofRioGrandeinWebbandZapatacounties). G.p.fallaxMerriam,1895—SportionsofSETexas(N&NWofNuecesBayalongthelowerNuecesRiver),USA.| G.p.fuscusDavis,1940—STexas(NofRioGrandeinKinneyandValverdecounties),USA. G.p.maritimusDavis,1940—GulfcoastofSTexas(mainlandbetweenBaffinBayandFlourBluff),USA. G. p. megapotamus Davis, 1940 — SE Texas, USA, into coastal NE Tamaulipas, Mexico. in Geomyidae
Subspecies and Distribution. G.p.personatusTrue,1889—MustangandPadreIs,KlebergCounty,Texas,USA. G.p.davisiWilliams&Genoways,1981—STexas,USA(NofRioGrandeinWebbandZapatacounties). G.p.fallaxMerriam,1895—SportionsofSETexas(N&NWofNuecesBayalongthelowerNuecesRiver),USA.| G.p.fuscusDavis,1940—STexas(NofRioGrandeinKinneyandValverdecounties),USA. G.p.maritimusDavis,1940—GulfcoastofSTexas(mainlandbetweenBaffinBayandFlourBluff),USA. G. p. megapotamus Davis, 1940 — SE Texas, USA, into coastal NE Tamaulipas, Mexico.
Subspecies and Distribution. I.a.auratusRamsay,1887—NWKimberleyandseveralsmallislandsoffKimberleycoast. I.a.arnhemensisLyne&Mort,1981—CapeArnhem,NENorthernTerritory. I. a. barrowensis Thomas, 1901 — Barrow I and Middle I, Western Australia. Occurs also (subspecies uncertain) on Marchinbar I, in Wessel Group, Northern Territory, and introduced recently to two further islands in Wessel Group. Barrow I race barrowensis introduced to nearby Hermite I, to Doole I (in Exmouth Gulf), and to Lorna Glen (mainland of C Western Australia) in recentyears. in Peramelidae
Subspecies and Distribution. I.a.auratusRamsay,1887—NWKimberleyandseveralsmallislandsoffKimberleycoast. I.a.arnhemensisLyne&Mort,1981—CapeArnhem,NENorthernTerritory. I. a. barrowensis Thomas, 1901 — Barrow I and Middle I, Western Australia. Occurs also (subspecies uncertain) on Marchinbar I, in Wessel Group, Northern Territory, and introduced recently to two further islands in Wessel Group. Barrow I race barrowensis introduced to nearby Hermite I, to Doole I (in Exmouth Gulf), and to Lorna Glen (mainland of C Western Australia) in recentyears.
Subspecies and Distribution. C.s.stuhlmanniiMatschie,1894—RwenzoriMts,NEDRCongoandSWUganda. C.s.balsac:Lamotte&Petter,1981—MtOku,WCameroon. C.s.fosteriSt.Leger,1931—MtElgon,EUganda,andCheranganiHills,WKenya. C.s.tropicalisG.M.Allen&Loveridge,1927—UluguruMtsandRungwedistrict,Tanzania. C. s. vermiculus Thomas, 1910 — known only from the vicinity of Yambuya and Kisangani, N DR Congo. in Chrysochloridae
Subspecies and Distribution. C.s.stuhlmanniiMatschie,1894—RwenzoriMts,NEDRCongoandSWUganda. C.s.balsac:Lamotte&Petter,1981—MtOku,WCameroon. C.s.fosteriSt.Leger,1931—MtElgon,EUganda,andCheranganiHills,WKenya. C.s.tropicalisG.M.Allen&Loveridge,1927—UluguruMtsandRungwedistrict,Tanzania. C. s. vermiculus Thomas, 1910 — known only from the vicinity of Yambuya and Kisangani, N DR Congo.
Distribution. Bahamas, only known from the type locality in East Plana Cay. Introduced into Little Wax Cay in 1973 and on Warderick Wells Cay in 1981, also in Bahamas. in Echimyidae
Distribution. Bahamas, only known from the type locality in East Plana Cay. Introduced into Little Wax Cay in 1973 and on Warderick Wells Cay in 1981, also in Bahamas.
Subspecies and Distribution. M.s.socialisPallas,1773—SEuropeanRussia(VolgogradandAstrakhanregionsandKalmykia)andWKazakhstan. M.s.aristoviGolenishchev,2002—E&SArmeniaandSAzerbaijan(includingNakhichevan). M.s.astrachanensisErxleben,1777—SEuropeanRussia. M.s.binominatusEllerman,1941—C&EGeorgia,NWArmenia,andNWAzerbaijan. M.s.bogdoensisWangFenggui&MaYong,1981—NWChina(CXinjiang). M.s.goriensisArgyropulo,1935—ETurkey. M.s.gravesiGoodwin,1934—C&EKazakhstan,NKyrgyzstan,NWTajikistan,andNWChina(extremeNWXinjang). M.s.hyrcanusGoodwin,1940—NW&NIran. M.s.nikolajeviOgnev,1950—UkraineandCrimea. M.s.parvusSatunin,1901—NCaucasus(RussiaandprobablyextremeNEAzerbaijan). M. s. zaitsevi Golenishchev, 2002 — E Azerbaijan. in Cricetidae
Subspecies and Distribution. M.s.socialisPallas,1773—SEuropeanRussia(VolgogradandAstrakhanregionsandKalmykia)andWKazakhstan. M.s.aristoviGolenishchev,2002—E&SArmeniaandSAzerbaijan(includingNakhichevan). M.s.astrachanensisErxleben,1777—SEuropeanRussia. M.s.binominatusEllerman,1941—C&EGeorgia,NWArmenia,andNWAzerbaijan. M.s.bogdoensisWangFenggui&MaYong,1981—NWChina(CXinjiang). M.s.goriensisArgyropulo,1935—ETurkey. M.s.gravesiGoodwin,1934—C&EKazakhstan,NKyrgyzstan,NWTajikistan,andNWChina(extremeNWXinjang). M.s.hyrcanusGoodwin,1940—NW&NIran. M.s.nikolajeviOgnev,1950—UkraineandCrimea. M.s.parvusSatunin,1901—NCaucasus(RussiaandprobablyextremeNEAzerbaijan). M. s. zaitsevi Golenishchev, 2002 — E Azerbaijan.
Subspecies and Distribution. A.f.fortisBuchner,1889—areasalongthegreatbendofHuangHeinChina(SpartsofInnerMongolia[=NeiMongol],Ningxia,Shaanxi,SEGansu,andNESichuan). A.f.calamorumThomas,1902—middleandlowerpartsofYangtzeRiverBasininS&EChina. A.f.dolichocephalusMori,1930—NEChina(EInnerMongolia,Jilin,andLiaoning). A.f.fujianensisHongZhenfan,1981—SEChina(NFujian). A.f.michnoiKastschenko,1910—SSiberiaandRussianFarEast(Transbaikalia,Amurarea,andNSakhalinI),N&NEMongolia,andNEChina(NInnerMongoliaandHeilongjiang). A. f. uliginosusJ. K. Jones & D. H. Johnson, 1955 — Korean Peninsula. in Cricetidae
Subspecies and Distribution. A.f.fortisBuchner,1889—areasalongthegreatbendofHuangHeinChina(SpartsofInnerMongolia[=NeiMongol],Ningxia,Shaanxi,SEGansu,andNESichuan). A.f.calamorumThomas,1902—middleandlowerpartsofYangtzeRiverBasininS&EChina. A.f.dolichocephalusMori,1930—NEChina(EInnerMongolia,Jilin,andLiaoning). A.f.fujianensisHongZhenfan,1981—SEChina(NFujian). A.f.michnoiKastschenko,1910—SSiberiaandRussianFarEast(Transbaikalia,Amurarea,andNSakhalinI),N&NEMongolia,andNEChina(NInnerMongoliaandHeilongjiang). A. f. uliginosusJ. K. Jones & D. H. Johnson, 1955 — Korean Peninsula.
Subspecies and Distribution. C.s.smithiiThomas,1895—EEthiopia. C. s. debalsaci Hutterer, 1981 — E Senegal. in Soricidae
Subspecies and Distribution. C.s.smithiiThomas,1895—EEthiopia. C. s. debalsaci Hutterer, 1981 — E Senegal.
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).
mosartwmpy tutorial data 1981-05
<p>Input data for following along with the mosartwmpy model tutorial: https://github.com/IMMM-SFA/mosartwmpy</p>
Supplementary material 2 from: Sidorov DA, Katz AD, Taylor SJ, Chertoprud MV (2016) A reassessment of the phylogenetic utility of genus-level morphological characters in the family Bogidiellidae (Crustacea, Amphipoda), with description of a new species of Eobogidiella Karaman, 1981. ZooKeys 610: 23-43. https://doi.org/10.3897/zookeys.610.9100
Figure S1 : Explanation note: Ordered bootstrap and jackknife consensus tree. Numbers below branches are bootstrap followed by jackknife support values.
Supplementary material 1 from: Sidorov DA, Katz AD, Taylor SJ, Chertoprud MV (2016) A reassessment of the phylogenetic utility of genus-level morphological characters in the family Bogidiellidae (Crustacea, Amphipoda), with description of a new species of Eobogidiella Karaman, 1981. ZooKeys 610: 23-43. https://doi.org/10.3897/zookeys.610.9100
Morphological character matrix : Explanation note: NEXUS file including character matrix for Bogidiellidae, Artesiidae and Kergueleniolidae used in analysis..
Supplementary material 3 from: Sidorov DA, Katz AD, Taylor SJ, Chertoprud MV (2016) A reassessment of the phylogenetic utility of genus-level morphological characters in the family Bogidiellidae (Crustacea, Amphipoda), with description of a new species of Eobogidiella Karaman, 1981. ZooKeys 610: 23-43. https://doi.org/10.3897/zookeys.610.9100
Figure S2 : Explanation note: Unordered bootstrap and jackknife consensus tree. Numbers below branches are bootstrap followed by jackknife support values.
FIGURE 18 in Redefinition of the genus Luciaphorus Mahunka, 1981 (Acari: Pygmephoridae) with redescription of L. perNiciosus Rack, 1983 and L. auriculariae Gao, Zou and Jiang, 1990
FIGURE 18. SEM micrograph of Luciaphorus auriculariae Gao, Zou and Jiang, 1990, female: A—pseudanal setae, B—leg I in ventral view, C—tibiotarsal claw, D—seta d on femur I.
FIGURE 17 in Redefinition of the genus Luciaphorus Mahunka, 1981 (Acari: Pygmephoridae) with redescription of L. perNiciosus Rack, 1983 and L. auriculariae Gao, Zou and Jiang, 1990
FIGURE 17. SEM micrograph of Luciaphorus auriculariae Gao, Zou and Jiang, 1990, female: A—dorsal view, B—ventral view, C—prodorsum, D—propodosomal plate, E—hysterosoma in ventral view, F—trichobothria.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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