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1,374 results for “Peninsular Malaysia”
Figure 2 from: Siti-Munirah MY, Dome N (2022) Thismia latiffiana (Thismiaceae), an unusual new species from Terengganu, Peninsular Malaysia. PhytoKeys 188: 105-114. https://doi.org/10.3897/phytokeys.188.77061
Figure 2 Thismia latiffiana, external morphology A roots B mature flower C apical part of floral tube with opening aperture D apex of mitre E ovary, side view F mature flower G trichomes resembling spines on an areole of cacti H mitre, side view. All from FRI91117: A, B, C, DFRI94686: E, F, G, H. Photos by Dome Nikong (A–D) and Siti-Munirah MY (E–H). Images not to scale (see dimensions in description and Figure 1).
Figure 1 from: Siti-Munirah MY, Dome N (2022) Thismia latiffiana (Thismiaceae), an unusual new species from Terengganu, Peninsular Malaysia. PhytoKeys 188: 105-114. https://doi.org/10.3897/phytokeys.188.77061
Figure 1 Illustration of Thismia latiffianaA habit, showing roots, young bud (Ai; note stems covered with trichomes), mature flower (Aii) and fruit (Aiii; note glabrescent stem with trichomes detached) B Leaf (adaxial) C bract (adaxial), smaller bract (Ci) D longitudinally dissected floral tube showing inner (abaxial) view of stamens and apical parts of connectives E portion of inner surface of floral tube (upper part) F trichomes on outer surface of floral tube; G outer (adaxial) view of stamens showing lateral appendages H stamen, view from below I gynoecium, longitudinal section, showing pistil with trilobed stigma and ovary J seed. All from FRI94686 (spirit material). Drawings by Mohamad Aidil Noordin.
Map 1 from: Siti-Munirah MY, Dome N (2022) Thismia latiffiana (Thismiaceae), an unusual new species from Terengganu, Peninsular Malaysia. PhytoKeys 188: 105-114. https://doi.org/10.3897/phytokeys.188.77061
Map 1 Map of Malay Peninsula with Hulu Nerus Forest Reserve (●), the type locality of Thismia latiffiana.
Supplementary material 1 from: Julius A (2022) Capparis (Capparaceae) in Peninsular Malaysia, including a new species and two new varieties. PhytoKeys 189: 99-127. https://doi.org/10.3897/phytokeys.189.49367
Figure S1–S8
Figure 8 from: Julius A (2022) Capparis (Capparaceae) in Peninsular Malaysia, including a new species and two new varieties. PhytoKeys 189: 99-127. https://doi.org/10.3897/phytokeys.189.49367
Figure 8 Capparis trinervia var. chungiana Julius, var. nov. A fruiting twig B stipular thorns C young fruit on stout gynophore D leaf E young fruit, cross section. (Photographs by K. Imin).
Figure 3 from: Julius A (2022) Capparis (Capparaceae) in Peninsular Malaysia, including a new species and two new varieties. PhytoKeys 189: 99-127. https://doi.org/10.3897/phytokeys.189.49367
Figure 3 Capparis kenaboiensis Julius, sp. nov. A habitat B fruiting branch C cross-section of fruit (upper left, the cut ripe fruit) D inflorescence E flower, front view F flower, lateral-abaxial view. (Photographs A–D by A. Julius and E–F by K. Imin).
Figure 2 from: Julius A (2022) Capparis (Capparaceae) in Peninsular Malaysia, including a new species and two new varieties. PhytoKeys 189: 99-127. https://doi.org/10.3897/phytokeys.189.49367
Figure 2 Capparis kenaboiensis Julius, sp. nov. A infructescence branch B inflorescence C flower D flower with sepals and petals removed exhibiting the stamens and ovary on gynophore E stamen F the outermost sepals pair G the dorsal petals H the ventral petals I the cross- and longitudinal-section of fruit J the stipular thorn close-up. (Drawn by Mohamad Aidil Noordin from FRI57784).
Figure 5 from: Julius A (2022) Capparis (Capparaceae) in Peninsular Malaysia, including a new species and two new varieties. PhytoKeys 189: 99-127. https://doi.org/10.3897/phytokeys.189.49367
Figure 5 Capparis scortechinii var. ruthiae Julius, var. nov. A flowering (bud) leafy twig with stipular thorns close-up next to it B flower bud close-up C flower bud with sepals and petals removed exhibiting the stamens D adaxial view of outer sepal (upper) and inner sepal (below) E dorsal petals, adaxial view (i) and abaxial view (ii) F ventral petals, exhibiting adaxial with hairs at base (left) and abaxial view (right) G flower bud dissected exhibiting one elongated stamen and the ovary on gynophore H anther, front (right) and back view (left) I fruit in cross-section and seeds (below) J an unguiculate leaf-like bract K venation close-up. (Drawn by Mohamad Aidil Noordin from Kiew RK3747 [A–H, J, L] and from Henderson 23551 [I]: the scale for C is similar to B).
Figure 7 from: Julius A (2022) Capparis (Capparaceae) in Peninsular Malaysia, including a new species and two new varieties. PhytoKeys 189: 99-127. https://doi.org/10.3897/phytokeys.189.49367
Figure 7 Capparis trinervia var. chungiana Julius, var. nov. A the leafy branch B the flowering (bud) leafy twig C flower with sepals and petals removed exhibiting the filaments and ovary on gynophore D upper pedicel and base of calyx E the fruit in cross section F stipules close-up. (Drawn by Mohamad Aidil Noordin from FRI64006 [A, E, F] and Mahmud Sidek s.n. [B–D]).
Distribution. Peninsular Thailand and Malaysia, and islands of Sumatra and Borneo. in Felidae
Distribution. Peninsular Thailand and Malaysia, and islands of Sumatra and Borneo.
Distribution. Peninsular Malaysia and W Borneo (Sarawak). in Vespertilionidae
Distribution. Peninsular Malaysia and W Borneo (Sarawak).
Distribution. Peninsular Malaysia and Sumatra in Hipposideridae
Distribution. Peninsular Malaysia and Sumatra
Number of terrestrial leeches with human-bait method and environmental variables in peninsular Malaysia
<p>This is the data on the number of terrestrial leeches (brown <em>Haemadipsa</em> sp.) collected and environmental variables at the sampling site in Endau Rompin National Park in Malaysia. <span>We investigated </span><span>relative abundance of terrestrial leeches repeatedly at </span><span>99 sampling points in the tourism area of ERNP from February 2019 to September 2020. </span><span>We counted the number of leeches at each sampling point based on the human-bait method, wherein the researcher is considered as the bait (Schnell et al. 2015, Fahmy et al. 2019). To activate the leeches before sampling, the leaf litter was blown upon and stirred with a twig in a 1.5-m radius from the sampling point. A researcher then stood at the sampling point and collected all the leeches attracted and attached to the body in a five-minute sampling session (Kendall</span><span>, 2012)</span><span>. We collected the leeches in a vial and measured the diameter of the sucking cup of each individual as a proxy for leech size: <1.5 mm = small, 1.5–3.0 mm = medium, and >3.0 mm = large. At the start of the sampling session, any leeches on </span><span>the researcher's body were removed and discarded. The leeches collected in the vial were all released at the sampling point after being counted and measured. Since leeches could detect host up to 2.0 m in our pilot survey, the relative abundance here can be regarded as a rough estimate of density of active leeches per 12.6 m<sup>2</sup> (an area within 2-m radius).</span></p> <p><span><span>The microenvironmental variables at each sampling point and time were measured to examine their effects on active leech relative abundance. These variables included air humidity, air temperature (°C), light intensity (lux), altitude (m), distance to the nearest river (m), distance to the nearest rain flow path (i.e., small valley through which water would flow in heavy rain) (m), percentage of bare ground (%), percentage of canopy openness (%), mean litter layer depth (mm), and topsoil moisture (%). Air humidity, air temperature</span><span>, and light intensity were measured using a handheld Illuminance UV recorder</span><span> (TR-74Ui</span><span>)</span><span>. The distances to the nearest stream and river were calculated using ArcMap 10.2.2. (ESRI Inc.</span><span>). The altitude was measured </span><span>using </span><span>a handheld Garmin geographic positioning system (GPS). The percentage of canopy openness and bare ground were measured using hemispherical photography via smartphone cameras equipped with "fisheye" lenses (Bianchi et al. 2017)</span><span> in </span><span>the near-vertical skyward and downward directions, respectively. The </span><span>litter layer depths were visually measured using a ruler. Soil moisture was measured directly at every sampling point using </span><span>a soil moisture meter (Takemura Soil Moisture Meter DM 18).</span> <span>The </span><span>percentages of bare ground, canopy openness, litter layer depth, and topsoil moisture, were recorded three times at randomly selected points around the sampling point</span><span>, and the average value was considered for the analyses</span><span>.</span></span></p> <p><span>To measure human and wildlife relative abundance, we installed passive infrared camera traps (O'Connell et al. 2011) (Ltl Acorn Ltl-6210MC, Cams Co., Ltd., Tokyo, Japan), which were triggered automatically by movement, at 24 on-trail sampling points. The camera was operated from February 2019 to September 2020 (560 days and 8,230 trap nights). The sampling points included trails with a gradient of tourist-use frequency. Each camera was mounted approximately 30–40 cm above the ground (Luo et al. 2019) to capture a wide range of animals of different sizes (Mugerwa et al. 2013). </span></p> <p><span><span> <span>The cameras were set up in video mode with 15 s in video length and 30 s in the interval between videos, which was sufficient to record </span><span>the group activity of potential hosts (wildlife or humans). </span><span>The number of individuals in each video</span><span> was counted. </span><span>To prevent double-counting individuals, a one-hour interval sequence was introduced between videos of a specific individual of the same species (Azlan & Sharma 2006). Each animal in the videos was identified at the species level</span><span>, based on </span><span>Francis (2008)</span><span>. Due to low image resolution, we could not identify small</span><span>er animals, such as </span><span>bats and rats at </span><span>the species level.</span></span></span></p>
Distribution. Malaysia (Cameron Highlands in Peninsular Malaysia). in Talpidae
Distribution. Malaysia (Cameron Highlands in Peninsular Malaysia).
Distribution. Mt Tahan and other peaks in Peninsular Malaysia. in Sciuridae
Distribution. Mt Tahan and other peaks in Peninsular Malaysia.
Distribution. Endemic to Peninsular Malaysia (Kedah, Perak, Kelantan, Pahang, and Selangorstates). in Soricidae
Distribution. Endemic to Peninsular Malaysia (Kedah, Perak, Kelantan, Pahang, and Selangorstates).
Distribution. Peninsular Thailand and Peninsular Malaysia. in Soricidae
Distribution. Peninsular Thailand and Peninsular Malaysia.
Distribution. Sumatra, SC Peninsular Malaysia, and N & C Borneo (including Balambangan I). in Muridae
Distribution. Sumatra, SC Peninsular Malaysia, and N & C Borneo (including Balambangan I).
Distribution. NW Peninsular Malaysia; perhaps extreme S peninsularThailand. in Muridae
Distribution. NW Peninsular Malaysia; perhaps extreme S peninsularThailand.
Distribution. Cameron Highlands, Peninsular Malaysia. in Muridae
Distribution. Cameron Highlands, Peninsular Malaysia.
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Allen Brain Atlas
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