Lithocarpus castellarnauianus
(S.Vidal) A.Camus
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
NT · Quasi menacéecritères B2b(iii)↘Décroissante- Évaluation
- 2020 · v3.1
- Altitude
- 60 – 2200 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
The species is reported to be abundant in its localities in Luzon however in other regions the species is more scarce (Soepadmo 1972). There is insufficient information to estimate the population size of the species, further research and study is needed. In 2019, Pro-Seeds Development Association, Inc. recorded three individuals of the species in Kasibu, Nueva Vizcaya, while a total of 25 individuals were recorded from the two hectares sampling plots in Mt. Calavite Wildlife Sanctuary in Mindoro. There is an expected decline in population due to continuing shifting agriculture, urbanization, and commodity-driven deforestation from the native provinces of the species. This is supported by 517,660 hectares of tree cover losses in just 18 years (GFW 2020) within the range of the species.
Menaces identifiées(4 menaces classées CMP-IUCN)
1_1Housing & urban areasOngoing2_1_1Shifting agricultureOngoing5_3_3Unintentional effects: (subsistence/small scale) [harvest]Ongoing5_3_4Unintentional effects: (large scale) [harvest]Ongoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Natural habitat loss is one of the main threats being faced by the species where expanding agricultural sites, urbanization, and uncontrolled logging activities are some of the major causes. This is supported by 2020 Global Forest Watch Analysis where 517,660 hectares of tree cover was lost from the range of the species from 2001 to 2018. This decline is continuing due to high statistics recorded until the past year. The species occurrence in some critical watersheds increases its vulnerability to population decline as these areas are increasingly subject to extensive human interventions which impair the overall capacity of the watershed in sheltering various endemic species. Some of these include Mounts Banahaw- San Cristobal Protected Landscape, Upper Agno River Basin Resource Reserve, and two other critical watersheds.
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
The natural occurrence of the species in some protected areas (PAs) offers protection to the species as these areas are supported by their respective implementing legislations under the National Integrated Protected Areas System Act of 1992 against excessive and unauthorized degradation and utilization. These PAs include Northern Sierra Madre Natural Park, Balbalasang-Balbalan National Park, in Mt. Calavite Wildlife Sanctuary and in five other PAs throughout the country.
Additionally, the species was also found to be present in some identified Philippine Key Biodiversity Area (KBAs), which are in Mts. Irid-Angilo and Binuang, Bataan Natural Park and Subic Bay Forest Reserve, Mt. Makiling Forest Reserve and two other KBAs. Though these sites are not officially protected by any implementing legislations, they are considered as top priority conservation areas where site-scale conservation efforts would be the best means for species and habitat protections (FPE 2020).
Actions de conservation (4)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection1_2Resource & habitat protection2_3Habitat & natural process restoration3_4_2Genome resource bank
Priorités de recherche (9)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_4Harvest, use & livelihoods1_5Threats1_6Actions3_1Population trends3_2Harvest level trends3_3Trade trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (12)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 10 December 2020).
- Energy Development Corporation (EDC). 2020. Biodiversity Assessment Reports.
- Foundation for the Philippine Environment (FPE). 2020. The Philippine Key Biodiversity Areas (KBAs). Available at: <a href="https://fpe.ph/biodiversity.html/view/the-philippine-key-biodiversity-areas-kbas">https://fpe.ph/biodiversity.html/view/the-philippine-key-biodiversity-areas-kbas</a>.
- GFW. 2020. Global Forest Watch. Available at: <a href="https://www.globalforestwatch.org/.">https://www.globalforestwatch.org/.</a>.
- Pro-Seeds Development Association, Inc. 2019. Biodiversity Assessment Reports.
- GBIF.org. 2019. GBIF Home Page. Available at: <a href="https://www.gbif.org/.">https://www.gbif.org/.</a>.
- Board of Trustees, RBG Kew. 2019. Plants of the World Online Portal. Richmond, UK . Available at: <a href="http://www.plantsoftheworldonline.org">http://www.plantsoftheworldonline.org</a>.
- Malabrigo, P.L., Jr. 2013. Vascular flora of the tropical montane forests in Balbalasang-Balbalan National Park, Kalinga Province, Northern Luzon, Philippines. <i>Asian Journal of Biodiversity</i> 4(294): 1-22.
- Pelser, P.B., Barcelona, J.F. and Nickrent, D.L. 2011. Co's Digital Flora of the Philippines. Available at: <a href="www.philippineplants.org">www.philippineplants.org</a>. (Accessed: 5 November 2014).
- Soepadmo, E. 1972. Fagaceae. <i>Flora Malesiana, II</i> 7(1): 358-359.
- Soepadmo, E. 1970. Florae Malesianae Precursoraes XLIX: Malesian Species of Lithocarpus Bl. (Fagaceae). <i>Reinwardtia,</i> 8(1): 197-308.
- Merrill, E.D. 1923. <i>Enumeration of Philippine Flowering Plants, II.</i> Manila Bureau of Printing, Manila.
Évaluateurs & contributeurs (3)Personnes ayant contribué à l'évaluation IUCNExpert
Energy Development Corporation (EDC) 2020. Lithocarpus castellarnauianus. The IUCN Red List of Threatened Species 2020: e.T138594364A138597955. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.
Consulter sur les bases externes
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (13)— redirigent vers cette page
- Lithocarpus cagayanensis(Merr.) A.Camus
- Lithocarpus merrittii(Merr.) Rehder
- Lithocarpus obliquinervis(Merr.) A.Camus
- Lithocarpus obliquinervius(Merr.) A.Camus
- Lithocarpus pinatubensis(Elmer) A.Camus
- Quercus cagayanensisMerr.
- Quercus castellarnauianaVidal
- Quercus castellnarnauianaS.Vidal
- Quercus merrittiiMerr.
- Quercus obliquinerviaMerr.
- Quercus pinatubensisElmer
- Synaedrys castellarnauiana(Vidal) Koidz.
- Synaedrys merrittii(Merr.) Koidz.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).