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170 results for “forest litter”
FIGURE 4 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 4. Olmeccyclops hondo sp. nov. A, leg 1, frontal view; B, leg 2, frontal view; C, leg 3, caudal view; D, leg 4, caudal view (endopodites illustrated detached, marked by arrows; A–C: female holotype, RBINSc COP 3936).
FIGURE 3 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 3. Olmeccyclops hondo sp. nov. A, antenna, caudal view; B, mandible; C, mandibular cutting edge, frontal view; D, maxillulary gnathobasis (dashed line indicates location of palp insertion); E, maxillulary palp; F, labrum; G, maxilla; H, maxillary endopodite, detached showing claw shaped aspect of terminal element; I, maxilliped, frontal view (A–I: female holotype, RBINSc COP 9936).
FIGURE 9 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 9. Moraria catracha sp. nov. A, baseoendopodite of leg 5, caudal view; B, leg 5, frontal view; C, leg 5, frontal view; D, genital and abdomal somites, ventral view; urosome, lateral view (A: female holotype, RBINSc 9944; B, female paratype, RBINSc COP 9945; C–E: male allotype, RBINSc COP 9946).
FIGURE 6 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 6. Moraria catracha sp. nov. A, antennule outline, ventral view; B, idem, exploded, showing setal armament; C, second and third antennulary segment, dorsal view (setae on ventral side not shown); D, antennule outline; E, antenna; F, maxillule; G, maxilla; H, maxilliped; I, mandible (palp detached) (E, F, I: female holotype, RBINSc COP 9944; A–C, B, G, H: female paratype, RBINSc COP 9945; D: male allotype RBINSc COP 9946).
FIGURE 1 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 1. Olmeccyclops hondo sp. nov. A, habitus, dorsal; B, apical setae of caudal ramus; C, anal somite and caudal rami, dorsal view; D, idem, dorsal view; E, rostrum, dorsal view; F, antennule, ventral view (A–C, E–F: female holotype, RBINSc COP 9936; D: female paratype, RBINSc COP 9937).
FIGURE 8 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 8. Moraria catracha sp. nov. A, leg 2, frontal; B, leg 3, frontal view; C, leg 4, frontal view; D, leg 2 endopodite, opposite side, frontal view; E, leg 2 endopodite, caudal view; F, leg 3 endopodite, caudal view; G, leg 4 endopodite, caudal view; H, idem, frontal view (A, D: female holotype, RBINSc COP 9944; B–C, female paratype, RBINSc COP 9945; E–H, male allotype, RBINSc COP 9946).
FIGURE 11 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 11. Moraria cusuca sp. nov. A, leg 2, frontal view; B, leg 3, frontal view; C, leg 4, caudal view; D, leg 5, frontal view (A–D: female holotype, RBINSc COP 9939).
FIGURE 5 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 5. Moraria catracha sp. nov. A, female habitus, dorsal; B, principal setae of left caudal ramus; C, male habitus, dorsal; D, principal apical setae of right caudal ramus; E, male, rostrum, ventral view; F; male, anal somite and caudal rami, enlarged; G, female, anal somite and caudal rami, enlarged (A–B, E, G: female holotype, RBINSc COP 9944; C–D, F: male
FIGURE 2 in Leaf litter copepods from a cloud forest mountain top in Honduras (Copepoda: Cyclopidae, Canthocamptidae)
FIGURE 2. Olmeccyclops hondo sp. nov. A, urosome, ventral view; B, urosome, lateral view (A–B: female holotype, RBINSc COP 9936).
Figs. 14–15 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Figs. 14–15. Number of Coleoptera specimens obtained at predetermined time intervals in two trials to test ECOLI protocol. 14) Trial A, Coleoptera specimens obtained from Berleses and Winklers at the initial 24-hr interval, during the intermediate interval at 96 hrs, and at the terminal extraction interval of 216 hrs; 15) Trial B, Coleoptera specimens obtained from Berleses and Winklers at the initial 24-hr interval and the terminal extraction interval of 216 hrs following an intermediate resting period from 24–96 hrs.
Figs. 12–13 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Figs. 12–13. Accumulation of specimens of Curculionidae obtained from six litter samples across extraction intervals. 12) Berlese funnels; 13) Winkler funnels.
Figs. 8–9 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Figs. 8–9. Accumulation of specimens of "rare" Coleoptera species obtained from six litter samples across extraction intervals. 8) Berlese funnels; 9) Winkler funnels.
Figs. 6–7 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Figs. 6–7. Accumulation of Coleoptera species obtained from six litter samples across extraction intervals. 6) Berlese funnels; 7) Winkler funnels.
Figs. 10–11 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Figs. 10–11. Accumulation of specimens of Staphylinidae obtained from six litter samples across extraction intervals. 10) Berlese funnels; 11) Winkler funnels.
Figs. 2–3 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Figs. 2–3. Flow chart diagramming test of ECOLI protocol. 2) Trial A, sample continuously run with three extraction intervals at 24, 96, and 216 hrs; 3) Trial B, sample run with initial collection interval at 24 hrs, "resting" period from 24–96 hrs, and terminal extraction interval at 216 hrs.
Fig. 1 in "Berlese vs. Winkler": Comparison of Two Forest Litter Coleoptera Extraction Methods and the Ecoli (Extraction of Coleoptera in Litter) Protocol
Fig. 1. Map of the southern United States showing locations of litter sample field sites. Polk County, Arkansas; West Feliciana Parish, Louisiana; Winston County, Alabama; Cochise County, Arizona; Swain County, North Carolina; Hidalgo County, New Mexico; Sabine County, Texas.
Litter–trapping tank bromeliads in five different forests: carbon and nutrient pools and fluxes
Bromeliads are the most abundant litter–trapping plants in Neotropical forest canopies. By intercepting litter, bromeliads obtain and retain nutrients before they reach the pedosphere. Here, we analyzed the litter captured and stored by tank bromeliads (TB) in five different forests along an elevation gradient in Mexico. Among those forests, carbon and nutrient pools and nitrogen fluxes in TB were estimated in a mangrove (MF) and a semi–deciduous tropical forest (SDTF). The composition of the litter trapped by TB along the gradient was similar to forest litterfall and was mainly composed of leaves. Most of the litter was captured in the dry season and we found a significant effect of projected plant area and the interaction between month and site on bromeliad litter capture. Moreover, litter stored in TB increased exponentially with projected plant area and differed between three studied species. In the MF (with ca. 2,700 TB ha<sup>-1</sup>), barely ca. 1% of annual litterfall is trapped by these plants, but even in the SDTF, with >10,000 TB ha<sup>-1</sup>, only ca. 2.4% is captured. We found that carbon and nitrogen pools in TB were small and represented < 1% of the carbon and nitrogen stored in forest aboveground biomass. Furthermore, the residence time of litter trapped in TB was not particularly large and was similar to that of litter on the forest floor. In light of our results, we conclude that in the studied forests the effect of TB on the forest carbon and nutrient cycle is negligible.
Distribution. Mt Cameroon, W Cameroon, and Bioko I, Equatorial Guinea. Descriptive notes. Head-body 100- 130 mm, tail 110-147 mm, ear 16-20 mm, hindfoot 21-25 mm; weight 27-62 g. Fur of the Cameroon Soft-furred Mouse is dark rufous-brown to blackish brown above and pale to dark gray below. Tail is very long (c.112% of head-body length) and dark. Hindfeet and forefeet are dark brown. Females have three pairs of nipples. Habitat. Montane forest and alpine grassland at elevations above 1000 m. Food and Feeding. No information. Breeding. Gestation lasts 26-30 days. Litters have 2-6 young. Activity patterns. The Cameroon Soft-furred Mouse is nocturnal and terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List. The Cameroon Soft-furred Mouse occurs in two disjunct areas occupying only ¢.2900 km? and the extent and quality of its forest habitat continue to decline. Bibliography. Eisentraut (1970, 1973), Happold (2013a), Missoup et al. (2012), Monadjem etal. (2015). in Muridae
Distribution. Mt Cameroon, W Cameroon, and Bioko I, Equatorial Guinea. Descriptive notes. Head-body 100- 130 mm, tail 110-147 mm, ear 16-20 mm, hindfoot 21-25 mm; weight 27-62 g. Fur of the Cameroon Soft-furred Mouse is dark rufous-brown to blackish brown above and pale to dark gray below. Tail is very long (c.112% of head-body length) and dark. Hindfeet and forefeet are dark brown. Females have three pairs of nipples. Habitat. Montane forest and alpine grassland at elevations above 1000 m. Food and Feeding. No information. Breeding. Gestation lasts 26-30 days. Litters have 2-6 young. Activity patterns. The Cameroon Soft-furred Mouse is nocturnal and terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Endangered on The IUCN Red List. The Cameroon Soft-furred Mouse occurs in two disjunct areas occupying only ¢.2900 km? and the extent and quality of its forest habitat continue to decline. Bibliography. Eisentraut (1970, 1973), Happold (2013a), Missoup et al. (2012), Monadjem etal. (2015).
Deccan region, Madras, India. Genus Vandeleuria is masculine, so widely used specific name oleracea has been changed for gender agreement. Vandeleuria oleraceusis possibly a composite of species. Polytypic, but subspecific taxonomy requires reassessment. Distribution. Widespread in S Asia (India, Nepal, Bhutan, Bangladesh, and Sri Lan-ka), S China (W & S Yunnan), and mainland SE Asia N of the Isthmus of Kra. Descriptive notes. Head-body 68 mm, tail 105 mm, ear 13 mm, hindfoot 17 mm; weight 10 g. The Indomalayan Long-tailed Climbing Mouse is small, with flat nail on outer finger and outertoe; tail is slender, brown, twice as long as head-body length, and lacks distal tuft. Dorsal pelageis silky and salmon in color; venter is white, with fulvous hues. Habitat. Tall cane and tangled vines in primary and secondary forest such as bamboo forest, moist deciduous forest, temperate forests, montane wet zone, and disturbed secondary forests, and perhaps agricultural areas at elevations of 150-1500 m. Food and Feeding. Indomalayan [Long-tailed Climbing Mice eat fruits, buds, and flowers. Breeding. Litters of the Indomalayan Long-tailed Climbing Mouse have 3-6 young. Activity patterns. Indomalayan Long-tailed Climbing Mice are arboreal and nocturnal, although one individual was caught duringthe day. Movements, Home range and Social organization. Indomalayan Long-tailed Climbing Mice build nests in tall bushes or cane to rear their young. Status and Conservation. Classified as Least Concern on The IUCN Red Last (as V. olacea). The Indomalayan Long-tailed Climbing Mouse occurs in several habitats and a wide distribution that includes national parks. Further taxonomical studies are required to assess conservation status ofthis potentially diverse species complex. Bibliography. Corbet & Hill (1992), Dang Huy Huynh et al. (1994), Ellerman (1941), Marshall (1977b), Musser & Carleton (2005), Osgood (1932), Phillips (1980), Wang Yingxiang (2003). in Muridae
Deccan region, Madras, India. Genus Vandeleuria is masculine, so widely used specific name oleracea has been changed for gender agreement. Vandeleuria oleraceusis possibly a composite of species. Polytypic, but subspecific taxonomy requires reassessment. Distribution. Widespread in S Asia (India, Nepal, Bhutan, Bangladesh, and Sri Lan-ka), S China (W & S Yunnan), and mainland SE Asia N of the Isthmus of Kra. Descriptive notes. Head-body 68 mm, tail 105 mm, ear 13 mm, hindfoot 17 mm; weight 10 g. The Indomalayan Long-tailed Climbing Mouse is small, with flat nail on outer finger and outertoe; tail is slender, brown, twice as long as head-body length, and lacks distal tuft. Dorsal pelageis silky and salmon in color; venter is white, with fulvous hues. Habitat. Tall cane and tangled vines in primary and secondary forest such as bamboo forest, moist deciduous forest, temperate forests, montane wet zone, and disturbed secondary forests, and perhaps agricultural areas at elevations of 150-1500 m. Food and Feeding. Indomalayan [Long-tailed Climbing Mice eat fruits, buds, and flowers. Breeding. Litters of the Indomalayan Long-tailed Climbing Mouse have 3-6 young. Activity patterns. Indomalayan Long-tailed Climbing Mice are arboreal and nocturnal, although one individual was caught duringthe day. Movements, Home range and Social organization. Indomalayan Long-tailed Climbing Mice build nests in tall bushes or cane to rear their young. Status and Conservation. Classified as Least Concern on The IUCN Red Last (as V. olacea). The Indomalayan Long-tailed Climbing Mouse occurs in several habitats and a wide distribution that includes national parks. Further taxonomical studies are required to assess conservation status ofthis potentially diverse species complex. Bibliography. Corbet & Hill (1992), Dang Huy Huynh et al. (1994), Ellerman (1941), Marshall (1977b), Musser & Carleton (2005), Osgood (1932), Phillips (1980), Wang Yingxiang (2003).
FIGURE 2. Albacillium hingganense. A in Albacillium hingganense gen. et sp. nov. (Clavicipitaceae) from forest litters in Northeast China
FIGURE 2. Albacillium hingganense. A, The front of colony in MEA. B. The reverse of colony in MEA. C. The front of colony in OA. D. The reverse of colony in OA. E. The front of colony in PDA. F. The reverse of colony in PDA. G. The front of colony in YMA. H. The reverse of colony in YMA. I. Conidia. J–Q. Hyphae, phialides, and conidia. J–P. Bars = 10 μm. Q. Bar = 50 μm.
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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
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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
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