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7,081 results for “Habitats”
Fig. 1 in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 1. Coastal waters of Bago City and the Municipality of Pulupandan in Guimaras Strait; Left inset: location of Western Visayas Region in the Philippines; Right inset: Guimaras Strait located between Negros Island and Guimaras Island.
Fig. 4. A in Habitat use and site fidelity of Irrawaddy dolphins (Orcaella brevirostris) in the coastal waters of Bago-Pulupandan, Negros Occidental, Philippines
Fig. 4. A, sightings of Irrawaddy dolphins (in yellow dots) relative to sectors; B, minimum convex polygon (MCP) of all sightings in Bago-Pulupandan coastal waters.
Fig. 2 in Home range, habitat use and roost-site selection by lowland female Siamese fireback Lophura diardi in northeastern Thailand
Fig. 2. The variation in home ranges and core areas of the eight female Siamese fireback in 2011 during different reproductive periods, estimated using 95% MCP and CHP Hot Spot methods. Locations shown were the food supplement sites (1 and 2) and nesting sites during the breeding season.
Fig. 3 in Home range, habitat use and roost-site selection by lowland female Siamese fireback Lophura diardi in northeastern Thailand
Fig. 3. The occurrence probability of Siamese fireback in relation to habitat variables. Shown are predicted values and 95% confidence limits for breeding (black solid lines) and non-breeding (gray dashed lines) periods.
Fig. 1 in Home range, habitat use and roost-site selection by lowland female Siamese fireback Lophura diardi in northeastern Thailand
Fig. 1. Location of Sakaerat Environmental Research Station (SERS), northeastern Thailand, including the locations of 60 available sites, two food supplementary sites, 14 nesting sites, and 52 roosting sites. Polygons shown are the home range boundaries of the eight radiotagged Siamese firebacks (group A–H).
Fig. 5 in The habitat preference of dung beetle species associated with elephant dung of the Malay Peninsula
Fig. 5. The Non-metric multidimensional scaling(NMDS) ordination of 25 species of dung beetle from 271 forest and forest edge sampling points. Filled squares represent species that prefer forest habitats, open squares represent species that prefer forest edge habitats, and crossed squares represent species that are evenly distributed among habitat types. Species codes: L.fem: Liatongus femoratus, On.tes: Oniticellus tessellatus, On.cinc: On. cinctus, Y.sar: Yvescambefortius sarawacus, O.babi: Onthophagus babirussa, O.rufi: O. rufiobscurior, O.vul: O. vulpes, O.ror: O. rorarius, O.prot: O. proletarius, O.pac: O. pacificus, O.rugi: O. rugicollis, O.ori: O. oreintalis, O.cras: O. crassicollis, O.lae: O. laevis, O.dayc: O. dayacus, O.kar: O. karenensis, O. lur: O. luridipennis, O.leu: O. leusermontis, O.viri: O. viridicervicapra, O.tsu: O. tsubakii, Cc.un: Caccobius unicornis, Ct.ren: Catharsius renaudpauliani, Cp.dor: Copris doriae, Cp.spi: Cp. spinator, M.brah: Megatelus brahminus.
Fig. 4 in The habitat preference of dung beetle species associated with elephant dung of the Malay Peninsula
Fig. 4. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) hierarchical clustering with Bray-Curtis distances of the 25 dung beetle species. Two major clusters are indicated, dung beetles that prefer (A) forest sampling points and (B) forest edge sampling points.
Fig. 2 in The habitat preference of dung beetle species associated with elephant dung of the Malay Peninsula
Fig. 2. Boxplots of the dung beetle relative abundance, species richness, and Shannon diversity for forest (n = 131) and forest edge (n = 140) sampling points.
Fig. 3. A in The habitat preference of dung beetle species associated with elephant dung of the Malay Peninsula
Fig. 3. A, Species accumulation curves for dung beetle species in 271 sampling points; B, Rarefaction curves comparing forest and forest edge samples. The solid line represents forest sampling points while the dotted line represents forest edge sampling points.
Fig. 4 in Sub-Montane Habitat Selection By A Lowland Pheasant
Fig. 4. The comparison of percentage tree cover (height>5 meters) between used areas during the three periods of the year cycle and random areas for Female 1 and Female 2 (a), and the comparison of tree density (height 0.5-3 meters) between used areas during the three periods and random areas for Female 1 and Female 2 (b).
Fig. 1. a in Sub-Montane Habitat Selection By A Lowland Pheasant
Fig. 1. a, Ranging size during different periods of the year cycle of Siamese Fireback, Female 1 and Female 2, estimated using 95% minimum convex polygons (MCP); b, 95 % MCP home range size compared in different phases of the year cycle between the two female Siamese Firebacks.
Fig. 2. A in Sub-Montane Habitat Selection By A Lowland Pheasant
Fig. 2. A comparison of slope in areas used during different periods of the year cycle and randomly chosen areas for Female 1 (a) and Female 2 (b).
Fig. 3 in Diel Variations And Diversity Of Fish Communities Along The Unreclaimed Shallow Coastal Habitats Of Changi Point Beach, Singapore
Fig. 3. Size class distribution of M. chinensis captured by day and night seines at Changi Point Beach between Oct. to Dec.2006 (error bars ± S.E.).
Fig. 2 in Diel Variations And Diversity Of Fish Communities Along The Unreclaimed Shallow Coastal Habitats Of Changi Point Beach, Singapore
Fig. 2. Size class distribution of P. quadrilineatus captured by day and night seines at Changi Point Beach between Oct. to Dec.2006 (error bars ± S.E.).
Fig. 4 in Diel Variations And Diversity Of Fish Communities Along The Unreclaimed Shallow Coastal Habitats Of Changi Point Beach, Singapore
Fig. 4. Size class distribution of H. cyanospilus captured by day and night seines at Changi Point Beach between Oct. to Dec.2006 (error bars ± S.E.).
Figure 1 in Variables Affecting Habitat Use Of Hume'S Pheasant In Two Disturbed Sites In Northern Thailand
Figure 1. Map showing the locations of Doi Chiang Dao and Mae- Lao Mae-Sae Wildlife Sanctuaries and Doi Khun Mae Daet located in northern Thailand.
Fig. 2 in Diel flight activity and habitat preference of dung beetles (Coleoptera: Scarabaeidae) in Peninsular Malaysia
Fig. 2. Mean number of (a) individuals; (b) species; and (c) biomass of dung beetles collected per hour during daytime (blank bar) and at night (solid bar) in the forest and open land. Error bars indicate standard errors. nsP≥0.05, *P<0.05, **P<0.01 (Kruskal-Wallis test).
Fig. 6 in Do habitat, month and environmental parameters affect shrimp assemblage in a shallow semi-enclosed tropical bay, Thailand?
Fig. 6. Biplots of some shrimp species and environmental variables (arrows) on the first two canonical axes derived from CCA of shrimp abundance and environmental variables in Pattani bay during February 2011 and January 2012.
Fig. 3 in Do habitat, month and environmental parameters affect shrimp assemblage in a shallow semi-enclosed tropical bay, Thailand?
Fig. 3. Relative density (%) and species richness of shrimps collected in different months in Pattani Bay between February 2011–January 2012 at five different habitats.
Fig. 4 in Do habitat, month and environmental parameters affect shrimp assemblage in a shallow semi-enclosed tropical bay, Thailand?
Fig. 4. Cluster dendogram demonstrating grouping of shrimps by month and habitat (Jan…Dec = January…December; Sa = sandy habitat, Ma = Mangrove habitat, S = Shell-deposited habitat, Mu = Muddy habitat and G = Seagrass habitat; G1, 2, 3 = cluster group 1, 2, and 3).
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Allen Brain Atlas
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International Brain Laboratory public data
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OpenNeuro
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