Ontologia

Boesenbergia belalongensis

A.D.Poulsen

LCLR Monde (IUCN)
Pays · région · aire protégée · écorégion · biome

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Calcul du tissu écologique de Boesenbergia belalongensis.

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Liste rouge IUCN

LC · Préoccupation mineure?Inconnue
Évaluation complète
Évaluation
2013 · v3.1
Altitude
65850 m
Profondeur
m
État de la populationExpert
The species was reported from several localities in the Batu Apoi Reserve from Kuala Belalong, at 65 m to about 850 m asl near Bukit Belalong (Poulsen 1993). In field surveys at different altitudes within the reserve, in 1994, the taxon wasn't found in the three plots sampled at 200 m asl, two individuals were found in one plot at 500 m asl and 40 individuals were found within the three surveyed plots at 850 m asl (Poulsen 1995). The size of the subpopulation near Bukit Madalon, in Sabah is unknown. The dynamics of the population are unknown.

Menaces identifiées(1 menace classée CMP-IUCN)

  • 7_1_3
    Trend Unknown/Unrecorded
    Ongoing
Description complète des menacesExpert
Over half of the lowland forest in Borneo has been converted or degraded due to human activities such as commercial and illegal logging, large-scale agriculture for oil palm, mining, dam construction, shifting cultivation and infrastructure development. Large fires have burnt several other remaining tracts. Many of Borneo's mountain forests have remained largely intact due to their isolation and the rugged landscape, but mining operations, large dams, high-altitude timber operations, and road building are all increasing threats to this ecoregion's biodiversity (Loucks 2001). However, the forest reserve of Bukit Belalong has continuous primary rainforest from its base to its summit (Pendry and Proctor 1997). Human impact on the forest is apparently slight and limited to hunting and gathering of forest products by local Iban People. The summit of Bukit Belalong has been cleared to allow helicopters to land and the clearing was extended to about 50 m x 50 m in January 1992 (Poulsen 1996). Deforestation in the Kinabalu area has slowed down considerably in the last decade. The park is proving to be effective in protecting the tropical forest against clearing. However, deforestation rates in the buffer zone have remained unchanged (Phua et al. 2008). Some species of Boesenbergia are used as spices and folk medicine and some have been found to have valuable medicinal properties, however, there is no recorded ethnobotanical use of this species. Gingers have enjoyed popularity as ornamental plants in Asia and the Far East for centuries. Ornamental gingers have rapidly increased in popularity in the western world in the past few years (West Demmy and Burch 1998), which has promoted an increase in illegal collecting. This is an attractive plant, with the central yellow-green leaves (Poulsen 1993), although it is not known whether extraction threatens the population of this species. Severe droughts have recently been affecting ecosystems in the region, however, the impact on this species is unknown.

Habitats préférentiels (classification IUCN)

  • 1_6Forest - Subtropical/Tropical Moist Lowland
Mesures de conservation recommandéesExpert
This species was collected within the Batu Apoi Forest Reserve, which covers 450 km2 of the Temburong district of Brunei and from within the Mount Kinabalu National Park, a World Heritage site in Sabah, which covers 754 km2. Habitats within these conservation units seem to have remained intact. Zingibericeae have often not been well explored in the field as collections were avoided by conventional workers due to the large herbaceous size, having fleshy rhizomes which pose a problem in the preparation of herbarium specimens. Additionally their occurrence as undergrowth in inaccessible forest areas can make collection difficult and the often short period of flowering hinders collection of materials with adequate character details (Prakash and Mehrotra 1996). Until recently, the region was largely botanically unexplored and under-collected and large tracts of montane rain forests still remain to be explored, it seems likely that many species may be incompletely mapped. Surveys should be conducted in historical sites of collection and potentially suitable areas to determine the current range and size of the population. The ecology and biology of the taxon should be studied and population viability analysis conducted. Seeds should be collected for germplasm conservation and cultivation as part of ex situ conservation measures. Collection of the taxon should otherwise be prohibited.
Actions de conservation (4)Expert
  • 1_1Site/area protection
  • 2_1Site/area management
  • 3_4_1Captive breeding/artificial propagation
  • 3_4_2Genome resource bank
Stress écologiques (1)Expert
  • 1_2Ecosystem degradation
Priorités de recherche (4)Expert
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Indomalayan

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Forb or Herb
Références bibliographiques (10)Expert
  1. IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.2). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 13 November 2013).
  2. Phua, M.H., Tsuyuki, S., Furuya, N. and Lee, J.S. 2008. Detecting deforestation with a spectral change detection approach using multitemporal Landsat data: A case study of Kinabalu Park, Sabah, Malaysia. <i>Journal of Environmental Management</i> 88(4): 784-795.
  3. Loucks, C. 2001. Borneo montane rain forests (IM0103).
  4. West Demmy, E. and Burch, D. 1998. Gingers - a Rising Star in Florida Gardens. <i>Proceedings of the Florida State Horticultural Society</i> 111: 190-191.
  5. Pendry, C.A. and Proctor, J. 1997. Altitudinal zonation of rain forest on Bukit Belalong, Brunei: soils, forest structure and floristics. <i>Journal of Tropical Ecology</i> 13(2): 221-241.
  6. Prakash, V. and Mehrotra, B.N. 1996. Zingiberaceae of North East India: diversity and taxonomic status. 2nd Symposium on the family Zingiberaceae. China.
  7. Poulsen, A.D. 1996. The herbaceous ground flora of the Batu Apoi Forest Reserve, Brunei, Darussalam. In: D.S. Edwards, W.E. Booth and S.C. Choy (eds), <i>Tropical rainforest research - current issues : proceedings of the Conference held in Bandar Seri Begawan, April 1993</i>, Kluwer Academic Publishers, Dordrecht ; London.
  8. Poulsen, A.D. and Pendry, C.A. 1995. Inventories of ground herbs at three alititudes on Bukit Belalong, Brunei, Borneo. <i>Biodiversity and Conservation</i> 4: 745-757.
  9. Poulsen, A.D. and Pendry, C.A. 1995. Inventories of ground herbs at three altitudes on Bukit Belalong, Brunei, Borneo. <i>Biodiversity and Conservation</i> 4: 745-757.
  10. Poulsen, A.D. 1993. Two new species of <i>Boesenbergia</i> (Zingiberaceae) from Borneo. <i>Nordic Journal of Botany</i> 13(3): 289-294.
Évaluateurs & contributeurs (2)Expert
assessor
Chadburn, H., Contu, S. & Romand-Monnier, F.
evaluator
Scott, J.A.

Chadburn, H., Contu, S. & Romand-Monnier, F. 2013. Boesenbergia belalongensis. The IUCN Red List of Threatened Species 2013: e.T44393569A44510279. Accessed on 05 May 2026.

Répartition mondiale (heatmap GBIF)Construction en cours

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Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

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