
Yucca brevifolia
Engelm.
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Calcul du tissu écologique de Yucca brevifolia.
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Liste rouge IUCN
LC · Préoccupation mineure↘Décroissante- Évaluation
- 2020 · v3.1
- Altitude
- 600 – 1800 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
This species can be common where it occurs. A recent species status assessment by the U.S. Fish and Wildlife Service (2018) concluded that Yucca brevifolia has a relatively large population and distribution, that covers a range of elevations with differing climatic conditions and soil types. For these reasons, they argued that Y. brevifolia subpopulations have:
(1) a high capacity to withstand or recover from stochastic disturbance events (resilience);
(2) the ability to recover from catastrophic events (redundancy); and
(3) can adapt to changing conditions (representation).
The age of first reproduction of Yucca brevifolia is estimated to be 60 years, based on an average growth rate of 3–4 cm per year (Comanor and Clark 2000, Esque et al. 2015) and the observed height of the plants when they first produce flowers (W. Hodgson and K. Clary pers. comm. 2019). The annual survival of the species is 0.992 (Gilliland et al. 2006). Therefore, the generation length of Y. brevifolia is calculated to be 185 years, using the following formula: generation length = 1/(1-annual survival) + age of first reproduction = 1/(1-0.992) + 60 = 185.
The extant Yucca brevifolia population covers 53,169 km2, and ~2,292 km2 have burned (4.31% of habitat since 1904). This was calculated by generating a fire footprint using data of fires from 1904 to 2019. The data was digitised resulting in a total of 1,073 polygons of areas affected by fire, 280 of which are prior 1980 and 513 are from 1980 to 2019, indicating a substantial increase in long-term fire frequency, which seems to be sustained by fire events in 2020. The fire footprint was overlaid with the species' range map to calculated the percentage of the range affected by fires. To calculate the species range decline we considered 115 years in the past, from the first records of fires in 1904, to 2089 for one generation (generation time = 185 years) and 30 years in the future to 2119 for the second generation, to meet the 100 years in future caveat from 2019. Therefore, considering 1.16 generations in the past and future, a 7.3% decline on the species range is predicted assuming fire events continue the same trend. This percentage decline, however, is likely an underestimate as fire events are increasing and droughts are predicted to worsen with climate change.
The study area in Gilliland et al. (2006) corresponds to the northeast Mojave Desert (even though the title of the paper says northwestern Mojave Desert) and therefore the species referred to in this study correspond to Y. jaegeriana (T.C. Esque pers. comm. 2020), however, given the similarity between Y. jaegeriana and Y. brevifolia, the information on annual survival can be used for both species (T.C. Esque pers. comm. 2020).
Menaces identifiées(8 menaces classées CMP-IUCN)
8_1_2Named speciesRapid DeclinesOngoing8_1_2Named speciesRapid DeclinesOngoing11_2DroughtsOngoing3_3Renewable energyOngoing5_2_2Unintentional effects (species is not the target)Ongoing7_1_1Increase in fire frequency/intensityOngoing8_2_2Named speciesOngoing8_2_2Named speciesOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
One of greatest threats to Yucca brevifolia and Y. jaegeriana subpopulations is high intensity and more frequent fires fuelled by exotic non-native annual grasses (primarily Red Brome (Bromus rubens) and secondarily Cheatgrass (Bromus tectorum)) (Brooks et al. 2013) that can kill or severely damage the plants, especially the smaller younger (shorter) individuals.
While Y. brevifolia is adapted to low intensity fires and can resprout from stems and rhizomes, the hotter and more frequent fires coupled with a unique life history strategy makes it difficult for Y. brevifolia to colonize burned landscapes (Abella 2010). Seed production does not occurs as masts (Borchert and DeFalco 2016) every year and depends on one known moth pollinator; ripe seeds must be freed from indehiscent fruits by small mammals to be dispersed and planted (Vander Wall et al. 2006, Waitman et al. 2012). The seeds germinate only under exacting rainfall and temperature conditions and quickly lose viability in soil if conditions are not met (Reynolds et al. 2012). The young plants are eaten by lagomorphs and rodents (Esque et al. 2015), so seedlings receive protection growing in association with native shrubs (Brittingham and Walker 2000), which are also decimated by fires. In conjunction with other stressors, including drought-induced increases in herbivory following wildfire and predicted higher temperatures from climate change, these factors collectively may contribute to population declines through time (DeFalco et al. 2010, St. Clair and Hoines 2018, U.S. Fish and Wildlife Service 2018).
More recent threats to this species include land clearing for energy development such as wind farms and in some areas solar farms.
For the portion of the range of the species within the Joshua Tree National Park, it has been predicted that without climate change mitigation the reduction of suitable habitat for the Joshua Tree would be such that it would go extinct by the year 2070 (Sweet et al. 2019). With moderately high and moderate climate change mitigation, refugia for 18.6% and 13.9% of the original occupied area, respectively, would remain as refugia (Sweet et al. 2019). However, this study provides evidence of the effects of climate change only in the southern (trailing edge) part of the species' range. Similar models are needed for the whole range of the species to have a complete representation of the climate variability across it and a better understanding of how the range of the species will be affected by climate change.
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate★3_5Shrubland - Subtropical/Tropical Dry★4_4Grassland - Temperate★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species occurs within the Joshua Tree National Monument, Mojave National Preserve, Grand Staircase-Escalante National Monument and Grand Canyon National Park.
Yucca brevifolia was determined on 2 January 2003 (and last reviewed) as having a Global Status level of G4, G5, with a Rounded Global Status of G4, being "Apparently Secure" according to NatureServe; the National Status: NNR, is N4 [note: this is the broader taxonomic concept as NatureServe does not recognise Y. jaegeriana] (NatureServe 2020).
A proposal to the U.S. Fish and Wildlife Service to consider listing the Joshua Tree (i.e. the broader taxonomic concept) under the U.S. Endangered Species Act was not successful (U.S. Fish and Wildlife Service 2019).
Yucca brevifolia and Y. jaegeriana are distinctly different species. Recognising them as such has significant implications for their management and conservation as they occupy different habitats and are mostly allopatric (W. Hodgson pers. comm. 2019).
Stress écologiques (30)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_3Indirect ecosystem effects1_3Indirect ecosystem effects2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance2_3_3Loss of mutualism2_3_3Loss of mutualism2_3_3Loss of mutualism2_3_4Loss of pollinator2_3_4Loss of pollinator2_3_4Loss of pollinator2_3_4Loss of pollinator
Usage & commerce (4)Use & Trade — IUCNExpert
13Pets/display animals, horticulturenational2Food - animal5Manufacturing chemicals8Fibresubsistance
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_1Taxonomy1_2Population size, distribution & trends1_3Life history & ecology2_1Species Action/Recovery Plan3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (30)Sources scientifiques de l'évaluation IUCNExpert
- NatureServe. 2020. NatureServe Explorer [web application]. NatureServe, Arlington, Virginia Available at: <a href="https://explorer.natureserve.org/">https://explorer.natureserve.org/</a>.
- 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).
- Sweet, L.C., Green, T., Heintz, J.G.C., Frakes, N., Graver, N., Rangitsch, J.S., Rodgers, J.E., Heacox, S. and Barrows, C.W. 2019. Congruence between future distribution models and empirical data for an iconic species at Joshua Tree National Park. <i>Ecosphere</i> 10(6): e02763.
- U.S. Fish and Wildlife Service. 2019. Iconic Joshua Tree Does Not Require Protection Under the Endangered Species Act. Available at: <a href="https://www.fws.gov/carlsbad/NR/JTree_12M_Finding_NR_final_20190814.pdf">https://www.fws.gov/carlsbad/NR/JTree_12M_Finding_NR_final_20190814.pdf</a>. (Accessed: August 14, 2019).
- St. Clair, S.B. and Hoines, J. 2018. Reproductive ecology and stand structure of Joshua tree forests across climate gradients of the Mojave Desert. <i>PLoS ONE </i> 13(2): e0193248. DOI: 10.1371/journal.pone.0193248.
- U.S. Fish and Wildlife Service. 2018. Joshua Tree Species Status Assessment. US Fish and Wildlife Service.
- Hawker, J. 2016. <i>Agaves, Yuccas and their kin; 7 genera of the Southwest</i>. Texas Tech University Press, Lubbock, TX.
- Borchert, M.I. and DeFalco, L.A. 2016. <i>Yucca brevifolia</i> fruit production, predispersal seed predation, and fruit removal by rodents during two years of contrasting reproduction. <i>American Journal of Botany</i> 103(5): 830–836.
- Esque, T., Medica, D., Shryock, L., Webb, R. and Hunter, R. 2015. Direct and indirect effects of environmental variability on growth and survivorship of pre-reproductive Joshua trees, <i>Yucca brevifolia<i> Englem. (Agavaceae). <i>American Journal of Botany </i> 102(1): 85–91.
- Brooks, M.L; Ostoja, S. and Klinger, R. 2013. Fire Effects on Seed banks and Vegetation in the Eastern Mojave Desert: Implications for Post-fire Management. U.S. Joint Fire Science Program. 81, Lincoln, Nebraska.
- Reynolds, M.B.J., DeFalco, L.A. and Esque, T.C. 2012. Short seed longevity, variable germination conditions, and infrequent establishment events provide a narrow window for <i>Yucca</i> brevifolia (Agavaceae) recruitment. <i>American Journal of Botany </i> 99(10): 1647–1654.
- Waitman, B.A , Vander Wall, S.B. and Esque, T.C. 2012. Seed dispersal and seed fate in Joshua tree (<i>Yucca brevifolia</i>). <i>Journal of Arid Environments</i> 81: 1–8.
- DeFalco, L., Esque, T., Scoles-Sciulla, S. and Rodgers, J. 2010. Desert wildfire and severe drought diminish survivorship of the long-lived Joshua tree (<i>Yucca brevifolia<i>; Agavaceae). <i>American Journal of Botany</i> 97(2): 243–250.
- Abella, S. 2010. Disturbance and plant succession in the Mojave and Sonoran Deserts of the American Southwest. <i>nternational Journal of Environmental Research and Public Health</i> 7: 1248–1284.
- Smith, C.I., Drummonds, C.S., Godsoe, W.K., Yoder, J.B. and Pellmyr, O. 2009. Host specificity and reproductive success of yucca moths (<i>Tegeticula</i> spp. Lepidoptera: Prodoxidae) mirror patterns of gene flow between host plant varieties of Joshua tree (Yucca brevifolia: Agavaceae). <i>Molecular Ecology</i> 18: 5218-5229.
- Lenz, L.W. 2007. Reassessment of Yucca brevifolia and Recognition of Y. jaegeriana as a Distinct Species. <i>Aliso: Journal of Systematic and Evolutionary Botany</i> 24(1): 97-104.
- Gucker, C.L. 2006. Yucca brevifolia. Available at: <a href="https://www.fs.fed.us /database/feis/plants/tree/yucbre/all.html">https://www.fs.fed.us /database/feis/plants/tree/yucbre/all.html</a>.
- Vander Wall, S.B., Esque, T., Haines, D., Garnett, M. and Waitman, B.A. 2006. Joshua tree (<i>Yucca brevifolia</i>) seeds are dispersed by seed-caching rodents. <i>Ecoscience </i> 13(4): 539–543.
- Gilliland, K.D., Huntly, N.J. and Anderson, J.E. 2006. Age and Population Structure of Joshua Trees (<i>Yucca brevifolia</i>) in the northwestern Mojave Desert. <i>Western North American Naturalist</i> 66(2): 202-208.
- Esque, TC., Haines, D.F, DeFalco, L.A., Rodgers, R.E., Goodwin, K.A. and Scoles, S.J. 2003. Mortality of adult Joshua trees (<i>Yucca brevifolia</i>) due to small mammal herbivory at Joshua Tree National Park, California. National Park Service, Great Basin Cooperative Ecosystem Studies Unit. University of Nevada, Reno.
- Pellmyr, O. and Segraves, K. 2003. Pollinator divergence within obligate mutualism: two yucca moth species (Lepidoptera; Prodoxidae: <i>Tegeticula<i>) on the Joshua tree (<i>Yucca brevifolia<i>; Agavaceae). <i>Annals of the Entomological Society of America </i> 96(6): 716-722.
- Hess, W. and Robbins, L.R. 2002. Yucca. In: Flora of North America Committee (ed.), <i>Flora of North America</i>, pp. 423-439. Oxford University Press, Oxford.
- Hodgson, W.C. 2001. <i>Food Plants of the Sonoran Desert</i>. University of Arizona Press.
- Comandor, P.L. and Clark, W.H. 2000. Preliminary growth rates and a proposed age-form classification for the Joshua Tree, <i>Yucca brevifolia</i> (Agavaceae). <i>Haseltonia</i> 7: 37–46.
- Brittingham, S. and Walker, L.R. 2000. Facilitation of <i>Yucca brevifolia</i> recruitment by Mojave Desert shrubs. <i>Western North American Naturalist </i> 60(4): 374–383.
- Comanor, P.L. and Clark, W.H. 2000. Preliminary growth rates and a proposed age‐form classification for the Joshua tree, <i>Yucca brevifolia</i> (Agavaceae). <i>Haseltonia</i> 7(7): 37– 46.
- Fowler, C. 1995. Some notes on ethnographic subsistence systems in Mojavean environments in the Great Basin. <i>Journal of Ethnobiology</i> 15(1): 99–117.
- Rowlands, P. 1978. The vegetation dynamics of the Joshua tree (<i>Yucca brevifolia</i> Engelmann) in the southwestern United States. University of California, Riverside.
- McCleary, J.A. 1973. Comparative Germination and Early Growth Studies of Six Species of the Genus Yucca. <i>The American Midland Naturalist</i> 90(2): 503-508.
- Zweifel, R.G. and Lowe, C.H. 1966. The ecology of a population of <i>Xantusia vigilis</i>, the desert night lizard. <i>American Museum Novitates</i> 2247: 1-57.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
Esque, T.C., DeFalco, L.A., Hodgson, W., Salywon, A., Puente, R. & Clary, K. 2020. Yucca brevifolia. The IUCN Red List of Threatened Species 2020: e.T117423077A117469962. Accessed on 05 May 2026.
Distribution mondiale
Phénologie
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Observations & statuts
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Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (16)— redirigent vers cette page
- Cleistoyucca arborescens(Torr.) Eastw.
- Cleistoyucca brevifolia(Engelm.) Rydb.
- Clistoyucca arborescens(Torr.) Trel.
- Clistoyucca brevifolia(Engelm.) Rydb.
- Sarcoyucca brevifolia(Engelm.) Linding.
- Yucca arborescens(Torr.) Trel.
- Yucca breviflora var. jaegerianaMcKelvey
- Yucca brevifolia f. herbertiiJ.M.Webber
- Yucca brevifolia subsp. brevifolia
- Yucca brevifolia subsp. herbertii(J.M.Webber) Hochstätter
- Yucca brevifolia var. brevifolia
- Yucca brevifolia var. herbertii(J.M.Webber) Munz
- Yucca brevifolia var. herbertiiEngelm.
- Yucca brevifolia var. wolfeiJones
- Yucca draconis var. arborescensL.
- Yucca draconis var. arborescensTorr.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).