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627 results for “Sabah”
Figs 16–20 in The Panjange nigrifrons group in Borneo (Araneae: Pholcidae): high diversity in Sarawak, apparent absence in Sabah
Figs 16–20. Panjange pueh Huber, sp. nov. (ZFMK Ar 14576–77). 16–17. Left male palp, prolateral and retrolateral views. 18. Male ocular area, clypeus, and chelicerae, oblique frontal view (arrow points at distal cheliceral apophysis). 19–20. Cleared female genitalia, ventral and dorsal views. Abbreviations: a = appendix; b = genital bulb; e = embolus; f = femur; p = procursus; ps = proximal bulbal sclerite; tr = trochanter. Scale lines: 0.5 mm.
Figs 33–34 in The Panjange nigrifrons group in Borneo (Araneae: Pholcidae): high diversity in Sarawak, apparent absence in Sabah
Figs 33–34. Panjange kapit Huber, sp. nov. (ZFMK Ar 14583). Left male palp, prolateral and retrolateral views. Abbreviations: a = appendix; b = genital bulb; e = embolus; f = femur; p = procursus; ps = proximal bulbal sclerite; tr = trochanter. Scale line: 1 mm.
Figs 52–60 in The Panjange nigrifrons group in Borneo (Araneae: Pholcidae): high diversity in Sarawak, apparent absence in Sabah
Figs 52–60. Female genitalia, untreated in ventral view, cleared in ventral and dorsal views. 52– 54. Panjange pueh Huber, sp. nov. (ZFMK Ar 14577). 55–57. Pa. niah Huber, sp. nov. (ZFMK Ar 14580). 58–60. Pa. kapit Huber, sp. nov. (ZFMK Ar 14584).
Figs 46–51 in The Panjange nigrifrons group in Borneo (Araneae: Pholcidae): high diversity in Sarawak, apparent absence in Sabah
Figs 46–51. Panjange kapit Huber, sp. nov. (ZFMK Ar 14583). 46. Male prosoma, frontal view. 47. Right distal male cheliceral apophysis. 48. Right procursus (and bulbal processes), dorsal view. 49. Ridges on left procursus, prolateral view. 50. Tip of left appendix, prolateral view. 51. Tip of left procursus (and embolus), ventral view. Abbreviations: a = appendix; e = embolus; p = procursus. Scale lines: 30 µm (47); 60 µm (50); 100 µm (49, 51); 200 µm (48); 400 µm (46).
Figs 8–15. Live specimens. 8–9 in The Panjange nigrifrons group in Borneo (Araneae: Pholcidae): high diversity in Sarawak, apparent absence in Sabah
Figs 8–15. Live specimens. 8–9. Panjange pueh Huber, sp. nov., Ƌ and ♀ from Pueh. 10–14. Pa. kapit Huber, sp. nov. from Kapit. 10–11. Adult Ƌ, 12. Penultimate instar Ƌ, 13–14. ♀ with egg-sac. 15. Pa. niah Huber, sp. nov., ♀ with egg-sac from Niah.
Figure 9 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 9. Map of the topography of our study area showing home ranges of five pairs of colour-banded Black-crowned Pittas Erythropitta ussheri observed in 2013. Coloured shapes represent the 95th percentile of a kernel density of sightings of each pair. Colours represent different pairs' territories. The location of a nest is marked by a yellow point. The map demonstrates the approximate number and size of Black-crowned Pitta home ranges, including apparent overlap between two pairs' home ranges. Kernel densities were calculated in R using the function kde2d with default bandwidth. We had only four sightings at one territory (maroon points near the upper left corner) and display points rather than kernel density. Grey lines represent trails, the brown line a pipeline, and the blue line the Tawau River. 3D map courtesy of JAXA (2015).
Figure 5 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 5. Banded Broadbill Eurylaimus javanicus nest during late construction, with an adult exiting at the lower left (© Kayleigh Chalkowski). Inset: close-up of the nest chamber after the nest was abandoned and collected, showing lining material (Eric R. Gulson-Castillo).
Figure 3 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 3. Black-and-yellow Broadbill Eurylaimus ochromalus nest, 2013 (Eric R. Gulson-Castillo). Inset: Black-and-yellow Broadbill holding a green object just before bringing it to its nest, from video ML 471552 (© Brian Magnier)
Figure 1 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 1. Map of the topography of our study area showing sightings of Black-and-yellow Eurylaimus ochromalus (blue) and Banded Broadbills E. javanicus (maroon) from both visits. Each point represents a sighting. Variation in point size and shape is an artefact of 3D plotting. This map demonstrates that Banded Broadbills occurred at a much-reduced density in the study area compared to Black-and-yellow Broadbills. Grey lines represent trails, the brown line represents a water pipeline, and the blue line represents the Tawau River. 3D map courtesy of JAXA (2015).
Figure 8 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 8. Graphical summary of nest visitation by Dusky Broadbills Corydon sumatranus during the early nestbuilding period. X axis = time of day. The thin blue line represents a continuous nest watch, the thicker lines visits by broadbills. The colour of each visit alternates to illustrate visits with short intervening breaks, which would otherwise appear to blend into a single line; colour does not represent sex or individual. Red line represents disturbance. We watched the nest until 18:00 h, but no birds visited after 14:21 h.
Figure 4 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 4. Graphical summary of nest visitation by Black-and-yellow Broadbills Eurylaimus ochromalus during incubation at one nest in 2013. Y axis = day (where day 68 = 9 March) and x axis = time of day. Thin blue lines represent time periods during which nest watches occurred, thicker lines represent visits by broadbills. Colour of thicker lines represents sex: pink = female, blue = male, dark grey = unsexed. Individuals could not always be sexed due to the angle that they approached the nest; these three colours probably represent just two individuals. When visit breaks are too short to be visible, they are marked with a small green line.
Figure 11 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 11. Map of the topography of our study area showing sightings of four species of pittas during the 2012 field work: Black-crowned Pitta Erythropitta ussheri (purple), Blue-headed Pitta Hydrornis baudii (blue), Bornean Banded Pitta H. schwaneri (yellow) and Blue-banded Pitta Erythropitta arquata (red). Each point represents a sighting. Variation in point size and shape is an artefact of 3D plotting. The map demonstrates that the areas occupied by each species overlapped considerably, especially on the ridge in the centre, where all four species occurred in close proximity. Black-crowned Pitta was seen more commonly in low swampy areas, whereas the other three species occurred mainly on this ridge and its slopes. A fifth species, Hooded Pitta Pitta sordida, was heard infrequently and seen just once, a juvenile, at the green point. Grey lines represent trails, the brown line a water pipeline, and the blue line the Tawau River. 3D map courtesy of JAXA (2015).
Figure 6 in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 6. Graphical summary of nest visitation by Banded Broadbills Eurylaimus javanicus during nest construction. Y axis = day (day 70 = 11 March) and x axis = time of day. Thin blue lines represent time periods during which nest watches occurred, thicker lines visits by broadbills. The colour of each visit alternates to highlight visits with short intervening breaks, which would otherwise appear to blend into a single line; colour does not represent sex or individual.
Figure 12. Two frames from a in Notes on nesting, territoriality and behaviour of broadbills (Eurylaimidae, Calyptomenidae) and pitas (Pitidae) in Tawau Hills Park, Sabah, Malaysian Borneo
Figure 12. Two frames from a video of an immature male Blue-headed Pitta Hydrornis baudii (top) showing a white throat, patches of blue in the underparts, and reddish wing-coverts, with an adult female Blue-headed Pitta (bottom). Frames from video ML 479513 (Justin Hite)
Fig. 2 in Molecular Identification, Fatty Acid Profile and Trace Elements in a Stranded Fin Whale in Sabah (Borneo, Malaysia): Implications on Migration Routes and Trophic Ecology of Southern Fin Whales.
Fig. 2. (a) The phylogenetic tree showing the stranded baleen whale (Baleen whale KP/Sabah/02082012) clustered together with the fin whale Balaenoptera physalus (U13103, Z18633 and X61145). (b) The phylogenetic analysis of the cytochrome b gene sequence indicating that the stranded fin whale (Baleen whale KP/Sabah/02082012) is closely related to the specimen of fin whales from the southern hemisphere with accession number KC572845, which represents Balaenoptera physalus quoi.
Fig. 1 in Molecular Identification, Fatty Acid Profile and Trace Elements in a Stranded Fin Whale in Sabah (Borneo, Malaysia): Implications on Migration Routes and Trophic Ecology of Southern Fin Whales.
Fig. 1. Stranding site (red-filled triangle) of the fin whale at the Sitompok River (Lat. 05°34'672"N; Long.115°39'710"E) near Kuala Penyu (KP), a coastal town overlooking the South China Sea on the western shores of Sabah (Borneo, Malaysia) (inset map). The approximate location of the sighting of possible fin whales reported by De Boer (2000) is marked with a blue-filled circle. The distribution ranges of rorquals species, including fin whales, in the Philippine waters reported by Slijper et al. (1964) and Acebes (2014) are marked with green-filled circles. The locations of fin whales' migration ranges in Australian waters according to Aulich et al. (2019) are shown using red-filled circles. The stranding site of the unconfirmed fin whale species at Pulau Sugi (Junge 1950) is indicated by a yellow-filled circle.
Fig. 4 in Molecular Identification, Fatty Acid Profile and Trace Elements in a Stranded Fin Whale in Sabah (Borneo, Malaysia): Implications on Migration Routes and Trophic Ecology of Southern Fin Whales.
Fig. 4. (a) Concentrations of trace elements (Mean ± SD) in the skin and blubber of the southern fin whale recorded in the present study compared to (b) the concentrations of trace elements in the skin of southern right whales (Eubalaena australis) extracted from the results of Martino et al. (2013).
Fig. 3 in Molecular Identification, Fatty Acid Profile and Trace Elements in a Stranded Fin Whale in Sabah (Borneo, Malaysia): Implications on Migration Routes and Trophic Ecology of Southern Fin Whales.
Fig. 3. Comparison of the percentages of fatty acid profiles for (a) SFA, (b) MUFA and (c) PUFA in the tissues of adult male (M) and female (F) southern humpback whales during the early and late migrations extracted from the results of Waugh et al. (2012), epipelagic and mesopelagic (i.e., average) fish in the South China Sea (SCS) extracted from the supplementary data of Wang et al. (2019) and the southern fin whale in the present study.
Impacts of rainforest degradation on the diets of the insectivorous bats of Sabah
<b>Description: </b><p>The work was carried out within Sabah, at the SAFE project, Danum Valley and Maliau basin. Bats were captured by deploying 6 harp traps per night, during field seasons taking place in 2015, 2016 and 2017. Bat guano samples were collected by placing individual bats into cloth bags, and then releasing them after 12 hours. Any guano in the bottom of the bag was then transferred into 95% ethanol and stored at -20. DNA was extracted from the faecal samples using a Qiagen Stool Mini kit, and then amplified using the ZBJ-ArtF1c ZBJ-ArtR2c primers, and sequencing the DNA on an Illumina MiSeq.</p><p><b>Project: </b>This dataset was collected as part of the following SAFE research project: <a href="https://www.safeproject.net/projects/project_view/182"><b>Impacts of rainforest degradation on the diets of the insectivorous bats of Sabah</b></a></p><p><b>Funding: </b>These data were collected as part of research funded by: </p><ul><li>NERC (Standard grant, NE/K016407/1)</li><li>Royal Society (Standard grant, RG130793)</li><li>Bat Conservation International (Standard grant)</li></ul><p>This dataset is released under the CC-BY 4.0 licence, requiring that you cite the dataset in any outputs, but has the additional condition that you acknowledge the contribution of these funders in any outputs.</p><p></p><p><b>Permits: </b>These data were collected under permit from the following authorities:</p><ul><li>Sabah Biodiversity Centre (Research licence JKM/MBS.1000-2/2 JLD.4 (46))</li></ul><p></p><p><b>XML metadata: </b>GEMINI compliant metadata for this dataset is available <a href="https://www.safeproject.net/datasets/xml_metadata?id=3247465">here</a></p><p><b>Files: </b>This dataset consists of 3 files: Bat_SAFE_data_metadata.xlsx, interaction_network.csv, sequences_95.fasta</p><p><b>Bat_SAFE_data_metadata.xlsx</b></p><p>This file contains dataset metadata and 1 data tables:</p><ol><li><p><b>data</b> (described in worksheet Data)</p><p>Description: measurements collected</p><p>Number of fields: 21</p><p>Number of data rows: 3292</p><p>Fields: </p><ul><li><b>TrapName</b>: The trap ID which the bats were captured in (Field type: ID)</li><li><b>Lat</b>: Latitude of trap (Field type: Latitude)</li><li><b>Long</b>: Longitude of trap (Field type: Longitude)</li><li><b>Elevation</b>: Elevation of trap (Field type: Numeric)</li><li><b>Bat_no</b>: Bat ID (Field type: ID)</li><li><b>Date</b>: Date of capture (Field type: Date)</li><li><b>Faeces_no1</b>: Tube number used to store faecal sample. Pairs up with column names of interaction matrix (Field type: ID)</li><li><b>Faeces_no2</b>: Number of any additional faeces (Field type: ID)</li><li><b>Biopsy_Dave</b>: Tube used to store wing biopsy (Field type: ID)</li><li><b>Block</b>: If sampling occurred within the SAFE landscape, this is the block it occurred within (Field type: ID)</li><li><b>Fragment</b>: If sampling occurred within the SAFE landscape, this is the fragment size it occurred within (Field type: ID)</li><li><b>Site</b>: The site within Sabah sampling occurred at (Field type: ID)</li><li><b>Species</b>: The bat species ID (Field type: Taxa)</li><li><b>Sex</b>: Male or Female (Field type: Categorical trait)</li><li><b>Age</b>: Was the bat an adult or juvenile (Field type: Categorical trait)</li><li><b>Forearm</b>: The forearm length of the bat (Field type: Numeric trait)</li><li><b>Weight</b>: The weight of the bat (Field type: Numeric Trait)</li><li><b>Reproductive_condition</b>: If a female bat, if the bat was Non-Reproductive, PRegnant, LActating or Post-Lactating (Field type: Categorical trait)</li><li><b>Parasite</b>: Tube used to store any ectoparasites obtained (Field type: ID)</li><li><b>Time</b>: If the bat was captured in evening or morning (Field type: Categorical)</li><li><b>Tag</b>: Band ID, if used (Field type: ID)</li></ul></li></ol><p><b>interaction_network.csv</b></p><p>Description: A network of operational taxonomic units found within the guano of bats captured in Sabah. The column names refer to the bat guano id, as found in the columns 'Faeces_no1' and 'Faeces_no2' in the fieldwork data, and the rownames refer to the OTU of the prey, which is paired to the names of the OTUs in the fasta file.</p><p><b>sequences_95.fasta</b></p><p>Description: A fasta file of prey OTUs found in bat guano, generated using 95% similarity for clustering. The sequence names correspond with the rownames of the file interaction_network.csv</p><p><b>Date range: </b>2015-02-16 to 2017-07-21</p><p><b>Latitudinal extent: </b>4.5000 to 5.0933</p><p><b>Longitudinal extent: </b>116.7500 to 117.8380</p><p><b>Taxonomic coverage: </b><br> All taxon names are validated against the GBIF backbone taxonomy. If a dataset uses a synonym, the accepted usage is shown followed by the dataset usage in brackets. Taxa that cannot be validated, including new species and other unknown taxa, morphospecies, functional groups and taxonomic levels not used in the GBIF backbone are shown in square brackets.</p><div>Animalia<br> - Chordata<br> -  - Mammalia<br> -  -  - Chiroptera<br> -  -  -  - Emballonuridae<br> -  -  -  -  - <i>Emballonura</i><br> -  -  -  -  -  - <i>Emballonura alecto</i><br> -  -  -  -  -  - <i>Emballonura monticola</i><br> -  -  -  - Hipposideridae<br> -  -  -  -  - <i>Hipposideros</i><br> -  -  -  -  -  - <i>Hipposideros ater</i><br> -  -  -  -  -  - <i>Hipposideros bicolor</i><br> -  -  -  -  -  - <i>Hipposideros cervinus</i><br> -  -  -  -  -  - <i>Hipposideros diadema</i><br> -  -  -  -  -  - <i>Hipposideros doriae</i><br> -  -  -  -  -  - <i>Hipposideros dyacorum</i><br> -  -  -  -  -  - <i>Hipposideros galeritus</i><br> -  -  -  -  -  - <i>Hipposideros ridleyi</i><br> -  -  -  - Megadermatidae<br> -  -  -  -  - <i>Megaderma</i><br> -  -  -  -  -  - <i>Megaderma spasma</i><br> -  -  -  - Nycteridae<br> -  -  -  -  - <i>Nycteris</i><br> -  -  -  -  -  - <i>Nycteris tragata</i><br> -  -  -  - Pteropodidae<br> -  -  -  -  - <i>Balionycteris</i><br> -  -  -  -  -  - <i>Balionycteris maculata</i><br> -  -  -  -  - <i>Macroglossus</i><br> -  -  -  -  -  - <i>Macroglossus minimus</i><br> -  -  -  -  - <i>Megaerops</i><br> -  -  -  -  -  - <i>Megaerops wetmorei</i><br> -  -  -  - Rhinolophidae<br> -  -  -  -  - <i>Rhinolophus</i><br> -  -  -  -  -  - <i>Rhinolophus acuminatus</i><br> -  -  -  -  -  - <i>Rhinolophus affinis</i><br> -  -  -  -  -  - <i>Rhinolophus borneensis</i><br> -  -  -  -  -  - <i>Rhinolophus creaghi</i><br> -  -  -  -  -  - <i>Rhinolophus luctus</i><br> -  -  -  -  -  - <i>Rhinolophus sedulus</i><br> -  -  -  -  -  - <i>Rhinolophus trifoliatus</i><br> -  -  -  - Vespertilionidae<br> -  -  -  -  - <i>Harpiocephalus</i><br> -  -  -  -  -  - <i>Harpiocephalus harpia</i><br> -  -  -  -  - <i>Hesperoptenus</i><br> -  -  -  -  -  - <i>Hesperoptenus blanfordi</i><br> -  -  -  -  - <i>Kerivoula</i><br> -  -  -  -  -  - <i>Kerivoula hardwickii</i><br> -  -  -  -  -  - <i>Kerivoula intermedia</i><br> -  -  -  -  -  - <i>Kerivoula lenis</i><br> -  -  -  -  -  - <i>Kerivoula minuta</i><br> -  -  -  -  -  - <i>Kerivoula papillosa</i><br> -  -  -  -  -  - <i>Kerivoula pellucida</i><br> -  -  -  -  -  - <i>Kerivoula whiteheadi</i><br> -  -  -  -  - <i>Murina</i><br> -  -  -  -  -  - <i>Murina aenea</i><br> -  -  -  -  -  - <i>Murina cyclotis</i><br> -  -  -  -  -  - <i>Murina rozendaali</i><br> -  -  -  -  -  - <i>Murina suilla</i><br> -  -  -  -  - <i>Myotis</i><br> -  -  -  -  -  - <i>Myotis muricola</i><br> -  -  -  -  -  - <i>Myotis ridleyi</i><br> -  -  -  -  - <i>Phoniscus</i><br> -  -  -  -  -  - <i>Phoniscus atrox</i><br> -  -  -  -  - <i>Pipistrellus</i><br> -  -  -  -  -  - <i>Pipistrellus javanicus</i><br> -  -  -  -  -  - <i>Pipistrellus tenuis</i><br> -  -  -  -  - <i>Scotophilus</i><br> -  -  -  -  -  - <i>Scotophilus kuhlii</i><br></div><p></p>
Fig. 2 in Camera-Trapping Survey Of Mammals In And Around Imbak Canyon Conservation Area In Sabah, Malaysian Borneo
Fig. 2. The observed species accumulation curve (-o-) and 95% CIs (---) for mammalian species in and around Imbak Canyon Conservation Area. The curve was constructed using abundancebased rarefaction approach (i.e., by using the number of independent photographs captured) with 100 randomisation runs in EstimateS (Colwell, 2009).
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