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464 results for “montane forest”
Figure 12 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 12. Flowers visited by thrips and bugs. (a, b) Chloranthus nervosus visited by thrips; (c) Mytilaria laosensis visited by thrips; (d, e) Dioscorea bulbifera visited by thrips; (f) Maesa sp., visited by a mecopteran; (g) Elatostema involucratum visited by a mirid bug; (h) Elatostema balansae visited by a mirid bug.
Figure 10 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 10. Flowers visited by beetles. (a, b) Fissistigma cupreonitens visited by chrysomelid beetles, an inner petal removed to show the inner chamber in (b); (c) Gentiana zollingeri visited by a scarabaeid beetle; (d) Melastoma malabathrica visited by scarabaeid beetles; (e) Photinia prunifolia visited by a scarabaeid beetle; (f) Lithocarpus elegans visited by a cerambycid beetle; (g) Euodia lepta visited by cerambycid beetles; (h) Photinia prunifolia visited by a cerambycid beetle; (i) Melastoma malabathrica visited by a meloid beetle, Mylabris phalerata; (j) Lithocarpus mucronata visited by a dermatid beetle; (k) Vitex leptobotrys visited by a curculionid beetle.
Figure 8 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 8. Flowers visited by small bees and wasps. (a) Embelia ribes visited by a stingless bee; (b) Thladiantha sp. visited by Ctenoplectra cornuta (visitor not in the photo); (c) Uncaria scandens visited by a halictid bee; (d) Sterculia henryi visited by a halictid bee; (e) Ludwigia hyssopifolia visited by a halictid bee; (f) Lysimachia siamensis visited by a Macropis orientalis bee; (g) Baliospermum montanum visited by a scoliid wasp; (h) Euphorbia lathyris visited by an ant; (i) Euodia lepta visited by an eumenid wasp; (j) Cynoglossum zeylanicum visited by an eumenid wasp; (k) Photinia prunifolia visited by an eumenid wasp.
Figure 2 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 2. Seasonal changes in monthly temperature (averages of monthly maximum, mean and minimum) and rainfall at Xam Neua near S4.
Figure 6 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 6. Flowers visited by honeybees: A. laboriosa (a–c), A. dorsata (d–f), Apis cerana (g–k) and A. florea (l). (a) Castanopsis diversifolia; (b) Castanopsis diversifolia; (c) Rubus multibracteatus; (d) Stachytarpheta jamaicensis; (E) Symplocos ramosissima; (f) Pogostemon nelsonii; (g) Ageratum houstonianum; (h) Photinia prunifolia; (i) Rubus obcordatus; (j) Bidens pilosa var. radiata; (k) Ixeris gracilis; (l) Photinia prunifolia.
Figure 3 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 3. Landscapes of the study sites S1–S5. (a) a meadow at S1; (b) paddy fields and secondary deciduous forests at S2; (c) a subtropical evergreen forest at S3; (d) a landscape at S4; (e) a valley inhabited by several Impatiens species at S4; (f) an evergreen oak forest near the summit of a mountain at S4; (g) a riverine forest inhabited by Mytilaria laosensis at S4; (h) limestone hills at S5.
Figure 11 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 11. Flowers visited by lepidopterans. (a) Isodon glaucocalyx visited by papilionid butterfly Papilio polytes; (b) Barleria cristata visited by a papilionid butterfly Papilio protenor; (c) Mussaenda cambodiana visited by a papilionid butterfly Troides helena; (d) Baliospermum montanum visited by a lycaenid butterfly Heliophorus epicles; (e) Lindera tonkinensis visited by a lycaenid butterfly Pithecos corbus; (f) Blumea martiniana visited by a nymphalid butterfly Zemeros flegyas; (g) Lindera tonkinensis visited by a nymphalid butterfly Yptima confusa; (h) Impatiens violaeflora visited by a hesperiid butterfly Onryza siamica; (i) Pottsia laxiflora visited by a pierid butterfly Appias albina; (j) Swertia aungustifolia visited by an arctiid moth and a hovering blue-banded Amegilla bee; (k) Ligustrum indicum visited by an arctiid moth.
Figure 16 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 16. The observed plant–pollinator network between flowers and eight groups of long-tongued bees. See Table 2 for plant species codes.
Figure 15 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 15. Flowers of eight observed Impatiens species (Bal1–Bal8): (a) I. chinensis; (b) I. commellinoides; (c) I. ernestii; (d) I. longiloba; (e) I. mengtszeana; (f) I. rubricolor; (g) I. tigrina; (h) I. violaeflora.
Figure 18 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem
Figure 18. Comparison of pollination systems among climatic and geographical regions: subalpine forests and meadows at Mt. Kushigata, central Japan (Kato 2000; Kato et al. 1993b), cool temperate deciduous forests at Ashu (Kato et al. 1990), warm temperate evergreen forest ecosystem at Amami Island (Kato 2000), montane evergreen forests in Laos (this paper), tropical monsoon forest ecosystem at lowland Laos (Kato et al. 2008), Bornean tropical rain forests at Lambir Hills National Park in Malaysia (Momose et al. 1998), and a Neotropical rain forest at La Selva (Kress and Beach 1994). The asterisk denotes large bees including long-tongued bees and carpenter bees.
Fig. 1 in Predation of the Rolled-Leaf Beetle Cephaloleia kressi García-Robledo (Coleoptera: Chrysomelidae: Cassidinae) by the Rove Beetle Phanolinus Sp. (Coleoptera: Staphylinidae: Xanthopygina) in a Montane Forest of Costa Rica
Fig. 1. Predation of Cephaloleia kressi by Phanolinus sp. A) Dorsal view of C. kressi, B) Heliconia lankesteri plant in situ, C) Phanolinus sp. predating on adult C. kressi, D) Body parts of C. kressi remaining after predation by Phanolinus sp.
Fig. 2 in Corrections and Additions to the Checklist of Bark and Ambrosia Beetles (Coleoptera: Curculionidae: Scolytinae, Platypodinae) of Mesic Montane Forest in Xalapa, Veracruz, Mexico
Fig. 2. Comparison of distribution patterns of species present in the Xalapa region based on 1990 and updated lists.
Fig. 1 in Corrections and Additions to the Checklist of Bark and Ambrosia Beetles (Coleoptera: Curculionidae: Scolytinae, Platypodinae) of Mesic Montane Forest in Xalapa, Veracruz, Mexico
Fig. 1. Broad biogeographical categories of genera and number of species in those genera for original and updated lists.
Response of Avian communities to edges of tropical montane forests: Implications for the future of endemic habitat specialists
<p>Tropical montane landscapes harbor diverse flora and fauna, and many species there are ecological specialists with narrow elevational distributions, limited geographic ranges, and small global populations. Along elevational gradients, environmental conditions and community composition change dramatically over small spatial scales. As forests are disturbed and edges formed with modified habitat, natural communities could be affected differently across elevations by the many physical and biotic changes at edges. We asked whether forest edges produced altered patterns of avian species composition along a cloud forest - dry forest gradient on the Pacific slope of the Tilarán mountains in Monteverde, Costa Rica. A strong moisture gradient produces cloud forests near the ridgetops, with a concentration of species endemic to the Costa Rica – Panama highlands that are habitat specialists. We conducted 552 point counts across 110 locations from 1100 to 1800 m elevation, yielding 6586 detections of 115 species in 10 km<sup>2</sup> of montane forest. We analyzed differences in species composition and single-species abundances between interior and near-edge forest habitats for species grouped by geographic range size. Species composition changed markedly from forest edge to interior in cloud forest habitats, but not in drier forests downslope. Endemic species, especially in cloud forest, were detected less frequently in mature forest near edges than in mature forest interior, and this difference was more pronounced than for cosmopolitan species. On tropical mountainsides, we can expect habitat-specialist endemic species to be more sensitive to further habitat modification. This sensitivity could limit the resilience of tropical bird communities.</p>
FIGURE 4. Carapa wohllebenii. A. Shoot with flowers. B. Inflorescence. C–F in Carapa wohllebenii (Meliaceae), a new tree species from montane forests in the Democratic Republic of Congo, Rwanda, and Burundi
FIGURE 4. Carapa wohllebenii. A. Shoot with flowers. B. Inflorescence. C–F. Flowers. Photographs: E. Fischer, Rwanda, Gisakura, 18 September 2016. Scale bars: A, C–F. 5 mm; B. 5 cm.
FIGURE 7 in Carapa wohllebenii (Meliaceae), a new tree species from montane forests in the Democratic Republic of Congo, Rwanda, and Burundi
FIGURE 7. Carapa grandiflora. Holotype in Herb. K. Reproduced with permission of the Board of Trustees, Royal Botanic Gardens, Kew.
FIGURE 3. Carapa wohllebenii. A, C. Branches with leaves and fruits. B in Carapa wohllebenii (Meliaceae), a new tree species from montane forests in the Democratic Republic of Congo, Rwanda, and Burundi
FIGURE 3. Carapa wohllebenii. A, C. Branches with leaves and fruits. B. Leaf. Photographs: E. Fischer. A. Rwanda, Uwinka, 24 September 2015. B. C. Butare, 3 January 2016. Scale bar: A. 10 cm; B, C. 5 cm.
FIGURE 6 in Carapa wohllebenii (Meliaceae), a new tree species from montane forests in the Democratic Republic of Congo, Rwanda, and Burundi
FIGURE 6. Carapa wohllebenii. Holotype in Herb. BR, inflorescence kept separate in spirit. Reproduced with permission of the Botanic Garden Meise.
FIGURE 2. Leaf and leaflet shape. A–B. Carapa wohllebenii. A. Bouxin 192. B. Fischer 758 in Carapa wohllebenii (Meliaceae), a new tree species from montane forests in the Democratic Republic of Congo, Rwanda, and Burundi
FIGURE 2. Leaf and leaflet shape. A–B. Carapa wohllebenii. A. Bouxin 192. B. Fischer 758/16 (holotype). C–D. Carapa grandiflora. C. Fischer 633/12. D. Dawe 351 (holotype). Drawings by D. Killmann. Scale bar: 5 cm.
FIGURE 10 in Carapa wohllebenii (Meliaceae), a new tree species from montane forests in the Democratic Republic of Congo, Rwanda, and Burundi
FIGURE 10. Known distribution of Carapa wohllebenii and Carapa grandiflora. Dots represent only the examined specimens. Carapa grandiflora is additionally represented by two further localities in southwestern Uganda and one in western Tanzania close to Lake Tanganyika (specimens not examined).
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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)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
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.