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53 results for “Mount Kinabalu”
Fig. 1 in A New Species Of Nabalua (Hemiptera: Cicadidae) From Mount Kinabalu, Borneo
Fig. 1: Nabalua gogalai, male holotype.
Elevational range-sizes and edaphic associations for plant species of the Mount Kinabalu region of Borneo (Sabah, Malaysia)
<p>Identifying physical and ecological boundaries that limit where species can occur is important for predicting how those species will respond to global change. The island of Borneo encompasses a wide range of habitats that support some of the highest richness on Earth, making it an ideal location for investigating ecological mechanisms underlying broad patterns of species distribution. We tested variation in richness and range-size in relation to edaphic specialization and vegetation zone boundaries using 3060 plant species from 193 families centered around the elevational gradient of Mt. Kinabalu, Borneo. Across species, average range-size increased with elevation, consistent with Rapoport's rule. However, plants associated with ultramafic soil, which is low in nutrient and water availability and often has high concentrations of heavy metals, had larger range-sizes and greater richness than expected along the elevational gradient, as compared to a null model with randomization of edaphic association. In contrast, non-ultramafic species had smaller range-sizes and lower richness than expected. These results suggest that tolerance of resource limitation may be associated with wider range-sizes, whereas species intolerant of edaphic stress may have narrower range-sizes, possibly owing to more intense competition in favorable soil types. Using elevation as a predictor of average range-sizes, we found that piece-wise models with breakpoints at vegetation zone transitions explained species distributions better than models that did not incorporate ecological boundaries. The greatest relative increases in range-size with respect to elevation occurred mid-elevation, within the montane cloud forest vegetation zone. Expansion of average range-size across an area without physical boundaries may indicate a shift in ecological strategy and importance of biotic versus abiotic stressors. Our results indicate that elevational range-size patterns are structured by ecological constraints such as species' edaphic association, which may limit the ability of species to migrate up or down mountains in response to climate change.</p>
Elevational range-sizes and edaphic associations for plant species of the Mount Kinabalu region of Borneo (Sabah, Malaysia)
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On following pages: 229. Bornean White-toothed Shrew (Crocidura foetida); 230. Kinabalu White-toothed Shrew Shrew (Crocidura orientalis); 233. Bangka White-toothed Shrew (Crocidura vosmaeri); 234. Hutan White-toothed White-toothed Shrew (Crocidura lepidura); 237. Mount Malindang White-toothed Shrew (Crocidura grandis); 238. 240. Panay White-toothed Shrew (Crocidura panayensis); 241. Negros White-toothed Shrew (Crocidura negrina); 242 Palawan White-toothed Shrew (Crocidura palawanensis); 245. Javan Long-tailed White-toothed Shrew (Crocidura (Crocidura horsfieldii); 248. Sinharaja White-toothed Shrew (Crocidura hikmiya); 249. Sri Lankan White-toothed Shrew White-toothed Shrew (Crocidura fuliginosa); 252. Large White-toothed Shrew (Crocidura dracula); 253. Sumatran dsinezumi); 255. Chinese White-toothed Shrew (Crocidura rapax); 256. Ussuri White-toothed Shrew (Crocidura lasiura (Crocidura zaitsevi); 259. Indochinese White-toothed Shrew (Crocidura indochinensis); 260. Hainan White-toothed Shrew (Crocidura maxi); 263. Javan Ghost White-toothed Shrew (Crocidura umbra); 264. Sunda White-toothed Shrew (Crocidura baluensis); 231. Thick-tailed White-toothed Shrew (Crocidura brunnea); 232. Oriental White-toothed Shrew (Crocidura hutanis); 235. Beccari's White-toothed Shrew (Crocidura beccarii); 236. Sumatran Giant Mindanao White-toothed Shrew (Crocidura beata); 239. Mindoro White-toothed Shrew (Crocidura mindorus);. Luzon White-toothed Shrew (Crocidura grayi); 243. Sibuyan White-toothed Shrew (Crocidura ninoyi); 244. abscondita); 246. Gathorne's White-toothed Shrew (Crocidura gathornei); 247. Horsfield's White-toothed Shrew (Crocidura miya); 250. Lesser Ryukyu White-toothed Shrew (Crocidura watasel); 251. Southeast Asian Long-tailed White-toothed Shrew (Crocidura paradoxura); 254. Dsinezumi White-toothed Shrew (Crocidura); 257. Asian Gray White-toothed Shrew (Crocidura attenuata); 258. Zaitsev's White-toothed Shrew Shrew (Crocidura wuchihensis); 261. Timor White-toothed Shrew (Crocidura tenuis); 262. Javan White-toothed (Crocidura monticola); 265. Neglected White-toothed Shrew (Crocidura neglecta). in Soricidae
On following pages: 229. Bornean White-toothed Shrew (Crocidura foetida); 230. Kinabalu White-toothed Shrew Shrew (Crocidura orientalis); 233. Bangka White-toothed Shrew (Crocidura vosmaeri); 234. Hutan White-toothed White-toothed Shrew (Crocidura lepidura); 237. Mount Malindang White-toothed Shrew (Crocidura grandis); 238. 240. Panay White-toothed Shrew (Crocidura panayensis); 241. Negros White-toothed Shrew (Crocidura negrina); 242 Palawan White-toothed Shrew (Crocidura palawanensis); 245. Javan Long-tailed White-toothed Shrew (Crocidura (Crocidura horsfieldii); 248. Sinharaja White-toothed Shrew (Crocidura hikmiya); 249. Sri Lankan White-toothed Shrew White-toothed Shrew (Crocidura fuliginosa); 252. Large White-toothed Shrew (Crocidura dracula); 253. Sumatran dsinezumi); 255. Chinese White-toothed Shrew (Crocidura rapax); 256. Ussuri White-toothed Shrew (Crocidura lasiura (Crocidura zaitsevi); 259. Indochinese White-toothed Shrew (Crocidura indochinensis); 260. Hainan White-toothed Shrew (Crocidura maxi); 263. Javan Ghost White-toothed Shrew (Crocidura umbra); 264. Sunda White-toothed Shrew (Crocidura baluensis); 231. Thick-tailed White-toothed Shrew (Crocidura brunnea); 232. Oriental White-toothed Shrew (Crocidura hutanis); 235. Beccari's White-toothed Shrew (Crocidura beccarii); 236. Sumatran Giant Mindanao White-toothed Shrew (Crocidura beata); 239. Mindoro White-toothed Shrew (Crocidura mindorus);. Luzon White-toothed Shrew (Crocidura grayi); 243. Sibuyan White-toothed Shrew (Crocidura ninoyi); 244. abscondita); 246. Gathorne's White-toothed Shrew (Crocidura gathornei); 247. Horsfield's White-toothed Shrew (Crocidura miya); 250. Lesser Ryukyu White-toothed Shrew (Crocidura watasel); 251. Southeast Asian Long-tailed White-toothed Shrew (Crocidura paradoxura); 254. Dsinezumi White-toothed Shrew (Crocidura); 257. Asian Gray White-toothed Shrew (Crocidura attenuata); 258. Zaitsev's White-toothed Shrew Shrew (Crocidura wuchihensis); 261. Timor White-toothed Shrew (Crocidura tenuis); 262. Javan White-toothed (Crocidura monticola); 265. Neglected White-toothed Shrew (Crocidura neglecta).
Phosphorus allocation to and resorption from leaves regulate the residence time of phosphorus in aboveground forest biomass on Mount Kinabalu, Borneo
<p>1. The residence time of phosphorus (P) in trees is a consequence of plant adaptation to P deficiency, with longer P residence time on soils with low P availability. P residence time has been studied at the leaf or canopy level but seldom at the whole-tree level. Whereas P residence time at the leaf or canopy level is largely determined by leaf longevity and the resorption of P before leaf abscission, P residence time at the whole-tree level will also be influenced by differences in P allocation to different plant parts because leaves and woody organs have distinct longevities.</p> <p>2. We estimated the residence time of P in aboveground tree biomass (AGB) as the ratio of P mass (i.e. leaves plus wood) to the annual flux of P via litterfall (i.e. fine litter plus coarse woody debris) for seven tropical rain forests with different soil P availabilities on Mount Kinabalu, Borneo. We analysed the effects of P allocation to and resorption from leaves on P residence time along a soil P gradient.</p> <p>3. P residence time (2.7–9.8 years) was approximately one fifth of biomass residence time (AGB/annual litterfall mass; 19.8–48.8 years). This was due to a disproportionately greater relative allocation of P to leaves (P mass in leaves/P mass in AGB; 0.11–0.46), which had a smaller fraction of biomass (leaf biomass/AGB; 0.02–0.05) but a shorter longevity (1.0–1.8 years).</p> <p>4. The relative allocation of P to leaves was often high on low-P soils, and P residence time was expected to be short. By contrast, the resorption rate of P from leaves was also high on low-P soils, which extended P residence time with P deficiency. Consequently, P residence time was nearly constant across the forests.</p> <p>5. The short residence time of P relative to biomass indicates that P residence time depends largely on relative P allocation among plant organs. Similar P residence times among sites were maintained because greater P allocation to leaves on low-P soils was effectively offset by higher P-resorption efficiency.</p>
FIGURE 2 in Gynura tambuyukonensis (Asteraceae), an obligate ultramafic species endemic to Mount Tambuyukon (Kinabalu Park, Sabah, Malaysia)
FIGURE 2. Gynura tambuyukonensis in the field. A Synflorescence; B Habit of plant creeping over bare ultramafic bedrock (peridotite); C Capitulum; D leaves. Photographs by Antony van der Ent.
FIGURE 1. Gynura tambuyukonensis. A in Gynura tambuyukonensis (Asteraceae), an obligate ultramafic species endemic to Mount Tambuyukon (Kinabalu Park, Sabah, Malaysia)
FIGURE 1. Gynura tambuyukonensis. A habit; B leaf; C capitulum; D phyllary; E floret with pappus; F style; G anthers; H cypsela. Illustration by Wanwisa Bhuchaisri and Pornphen Supachok.
FIGURES 40A–C. Africasia acuticoxalis n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 40A–C. Africasia acuticoxalis n. sp.. holotype female. A = dorsal view; B = ventral view; C = palp + capitulum. Scale bars = 50 Μm.
FIGURES 39A–D. Aturus borneoensis n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 39A–D. Aturus borneoensis n. sp., holotype male. A = dorsal view; B; C = palp; D = IV-leg-4–5. Scale bars = 50 Μm.
FIGURES 37A–C. Ljania obliterata n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 37A–C. Ljania obliterata n. sp., holotype female. A = dorsal view; B = ventral view; C = palp. Scale bars = 50 Μm.
FIGURES 36A–C. Ljania inconspicua n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 36A–C. Ljania inconspicua n. sp., holotype female. A = dorsal view; B = ventral view; C = palp. Scale bars = 50 Μm.
FIGURES 35A–D. Erebaxonopsis kipungitensis n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 35A–D. Erebaxonopsis kipungitensis n. sp., holotype male. A = dorsal view; B = ventral view; C = palp; D = IVleg-1–6. Scale bars = 50 Μm.
FIGURES 34A–D. Axonopsis caeca n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 34A–D. Axonopsis caeca n. sp., holotype female. A = dorsal view; B = ventral view; C = posterocaudal view; D = palp. Scale bars = 50 Μm.
FIGURES 33A–C. Axonopsis latipalpis n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 33A–C. Axonopsis latipalpis n. sp., holotype male. A = dorsal view; B = ventral view; C = palp. Scale bars = 50 Μm.
FIGURES 32A–G. Axonopsis truncata n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 32A–G. Axonopsis truncata n. sp., holotype male A–D, paratype male E, paratype female F–G. A = dorsal view; B, G = ventral view; C = posterocaudal view; D–E = palp; F = dorsal view. Scale bars = 50 Μm.
FIGURES 31A–C. Axonopsis rugosa n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 31A–C. Axonopsis rugosa n. sp., holotype female. A = dorsal view; B = ventral view; C = palp. Scale bars = 50 Μm.
FIGURES 30A–D. Axonopsis longigenitalis n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 30A–D. Axonopsis longigenitalis n. sp., holotype male. A = dorsal view; B = ventral view; C = palp; D = genital skeleton. Scale bars = 50 Μm.
FIGURES 29A–C. Albaxona mahuaensis n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 29A–C. Albaxona mahuaensis n. sp., holotype male. A = dorsal view; B = ventral view; C = palp. Scale bars = 50 Μm.
FIGURES 38A–D. Albia crocker n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 38A–D. Albia crocker n. sp., holotype male A–C, paratype female D. A = dorsal view; B, D = ventral view; C = palp. Scale bars A–B, D= 200 Μm, C = Μm.
FIGURES 28A–F. Javalbia uncinata n in Water mites from Mount Kinabalu and the Crocker Range, Borneo, Malaysia (Acari: Hydrachnidia), with the description of 34 new species
FIGURES 28A–F. Javalbia uncinata n. sp., holotype male. A = dorsal view; B = ventral view; C = I-leg-4-6; D = II-leg-5–6; E = IV-leg-4–6; F = palp. Scale bars = 50 Μm.
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