
Quercus emoryi
Torr.
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Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
LC · Préoccupation mineure→Stable- Évaluation
- 2017 · v3.1
- Altitude
- 1000 – 2800 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
No quantitative information on Quercus emoryi's population size exists, however Natureserve considers Q. emoryi's population to be sucure (G5).
Menaces identifiées(8 menaces classées CMP-IUCN)
2_3_2Small-holder grazing, ranching or farmingUnknownMinority (<50%)Ongoing5_2_1Intentional use (species is the target)UnknownUnknownOngoing5_3_1Intentional use: (subsistence/small scale) [harvest]UnknownMinority (<50%)Ongoing6_1Recreational activitiesUnknownMinority (<50%)Ongoing7_1_2Supression in fire frequency/intensityUnknownUnknownOngoing8_2_2Named speciesUnknownUnknownOngoing8_2_2Named speciesUnknownUnknownOngoing11_1Habitat shifting & alterationSlow, Significant DeclinesMajority (50-90%)Future
Description complète des menacesTexte détaillé évaluation IUCNExpert
Cattle grazing is common in oak woodlands where Emory Oak codominates, and conversion of pine-oak woodlands and chaparral stands to grassland for livestock has been common through Emory Oak's range. However, it seems this practice of clearing habitat for rangeland is slowing, at least in the United States. Harvest of Q. emoryi is a definite threat, and although there are regulations to protect against over-harvest for firewood within US National Forests, the rate of mortality for firewood, construction materials, as well as acorns for food, is unknown in the species' Mexican range. Heavy browsing by White-Tailed Deer (Odocoileus virginianus) and Mule Deer (Odocoileus hemionus) in combination with climate shifts towards hotter and dryer conditions have revealed in some cases a skewed age distribution where seedling recruitment of Q. emoryi is low to none. Fire suppression as well as recreational activities threaten Emory Oak as human populations increase in southern Arizona (Pavek 1994, Gottfried and Folliott 2013). Another major threat to Q. emoryi is climate change; in a study by Potter and Hargrove (2013) Quercus emoryi is projected to lose 45.48% of its suitable habitat area by 2050 under the the Hadley B1 Global Circulation Model/ scenario combination. A later study also used projection data along with species specific intrinsic traits to asses tree vulnerability in three areas: 1) exposure to climate change, which included projected area change by 2050 and distance to future habitat; 2) sensitivity to threat, which included rarity, area of distribution, dispersal ability, and disturbance tolerance; and 3) adaptability to threat, which included regeneration, genetic variability, and ecological requirements. Quercus emoryi was found to be a "potential persister" meaning it had high exposure to climate change pressure and low potential to adapt to that threat, but only moderate threat sensitivity. As such it may be able to may be able to withstand climate change in situ, because of its area of distribution, dispersal ability, and disturbance tolerance, but close monitoring will be required to verify this (Potter et al. 2017).
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate★3_4Shrubland - Temperate★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Quercus emoryi is located ex situ in 17 sites within botanic gardens and arboreta globally, according to Botanic Gardens Conservation International (2016).
Actions de conservation (2)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection2_1Site/area management
Stress écologiques (12)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_2Ecosystem degradation1_3Indirect ecosystem effects1_3Indirect ecosystem effects2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance
Usage & commerce (5)Use & Trade — IUCNExpert
1Food - humannationalsubsistance11Other household goodssubsistance2Food - animalsubsistance7Fuelsnationalsubsistance9Construction or structural materialssubsistance
Priorités de recherche (2)Research Needed Classification — IUCNExpert
3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Nearctic
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Shrub - largeTree - small
Références bibliographiques (11)Sources scientifiques de l'évaluation IUCNExpert
- BGCI. 2017. PlantSearch. Available at: <a href="www.bgci.org/plant_search.php">www.bgci.org/plant_search.php</a>.
- Potter, K., Crane, B. and Hargrove, W. 2017. A United States national prioritization framework for tree species vulnerability to climate change. <i>New Forests</i>: 1–26.
- NatureServe. 2003. <a href="http://www.natureserve.org/explorer">NatureServe Explorer: An online encyclopedia of life</a> [web application]. Version 1.8. NatureServe, Arlington, Virginia. (Accessed: October 20, 2003).
- IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 14 September 2017).
- IUCN. 2015. The IUCN Red List of Threatened Species. Version 2015-4. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 19 November 2015).
- Romero Rangel, S., Rojas Zenteno, E.C. and Rubio Licona, L.E. 2015. <i>Encinos de Mexico</i>. Universidad Nacional Autónoma de Mexico.
- GBIF. 2015. Global Biodiversity Information Facility (GBIF) Occurrence Download. Available at: <a href="http://www.gbif.org/">http://www.gbif.org/</a>. (Accessed: September 2015).
- Gottfried, G.J. and Ffolliott, P.F. 2013. Ecology and Management of Oak Woodlands and Savannas in the Southwestern Borderlands Region. USDA Forest Service.
- Potter, K.M and Hargrove, W.W. 2013. Quantitative Metrics for Assessing Predicted Climate Change Pressure on the North American Tree Species. <i>Mathematical and Computational Forestry and Natural-Resources Science</i> 5(2): 151-169.
- eFloras. 1997. Flora of North America. Vol. 3. Missouri Botanical Garden, St. Louis, MO & Harvard University Herbaria, Cambridge, MA Available at: <a href="http://www.efloras.org/volume_page.aspx?volume_id=1003&flora_id=1">http://www.efloras.org/volume_page.aspx?volume_id=1003&flora_id=1</a>. (Accessed: 2015).
- Pavek, D.S. 1994. <i>Quercus emoryi</i>. In: Fire Effects Information System, [Online] . Available at: <a href="http://www.fs.fed.us/database/feis/plants/tree/queemo/all.html#38">http://www.fs.fed.us/database/feis/plants/tree/queemo/all.html#38</a>. (Accessed: October 2015).
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Beckman, E. & Jerome, D.
evaluator
Oldfield, S.
Beckman, E. & Jerome, D. 2017. Quercus emoryi. The IUCN Red List of Threatened Species 2017: e.T194126A111335378. 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
Observations & statuts
Cartographie
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (6)— redirigent vers cette page
- Quercus balsequillanaTrel.
- Quercus duraznilloTrel.
- Quercus duraznillo f. bullataTrel.
- Quercus duraznillo f. cochutensisTrel.
- Quercus duraznillo f. pinetorumTrel.
- Quercus hastataLiebm.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).