Yucca jaegeriana

(McKelvey) L. W. Lenz

Eastern Joshua Tree

G3Vulnerable (G3G4) Found in 15 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
High - mediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.156126
Element CodePMAGA0B072
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassMonocotyledoneae
OrderAsparagales
FamilyAsparagaceae
GenusYucca
Synonyms
Yucca brevifolia var. jaegerianaMcKelvey
Other Common Names
Jaeger's Joshua tree (EN) Jaeger's Joshua Tree (EN)
Concept Reference
Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Taxonomic Comments
Yucca brevifolia var. jaegeriana was described in 1938, and considered a distinct taxon through the late 1970s, until J. L. Reveal treated it no longer distinct from the type. Flora North America (2002a) follows the J. L. Reveal treatment. In 2007, however, it was described as the species level (Lenz 2007a). Morphological, biological (pollination), and genetic studies, support the distinctiveness of this entity and recognition at the specific rank (Royer et al. 2016 and Lenz 2007a). The U.S. Fish and Wildlife Service recognize Yucca jaegeriana and Yucca brevifolia as distinct species (USFWS 2019).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2021-02-02
Change Date2021-02-02
Edition Date2021-02-02
Edition AuthorsTreher (2021)
Threat ImpactHigh - medium
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Rank Reasons
Yucca jaegeriana, Eastern Joshua Tree, is an iconic species and near endemic of the Mojave Desert of the southwestern United States, with occurrences in Arizona, California, Nevada, and Utah. It is threatened by fire, drought, climate change, and numerous threats related to habitat loss including off road vehicle use
Range Extent Comments
Yucca jaegeriana is endemic to the United States and occurs primarily within the Mojave Desert including areas of western Arizona, southeastern California, southern Nevada, and extreme southwestern Utah. To the north, the species range falls within the Great Basin Desert and to the east in Sonoran Desert of Arizona (USFWS 2018). This species overlaps in range with Yucca brevifolia in a small area of Nevada, called the Tikaboo Valley, where the two species hybridize (Royer et al. 2016, Lenz 2007). Range extent was calculated using data from iNaturalist (2021), SEINet (2021), and CCH2 (2021).
Threat Impact Comments
Yucca jaegeriana is threatened by fire, drought, climate change, and numerous threats related to habitat loss. One of the more severe threats to the species is an increase in fire frequency, which causes direct mortality and reduced survivorship over time. A greater presence of non-native annual grasses, which produce a fuel load in the environment, have increased the frequency of fire in the deserts where this species occurs. The plant communities and Joshua Tree itself are not especially tolerant of fire. Native plants, when responding with vigorous growth to an unusually wet winter, also contribute to an increased fuel load and are responsible for some fires in the past. Younger, smaller plants are more vulnerable to mortality than older, larger plants. One cause of mortality post-fire is predation by small mammals seeking a food source (USFWS 2018, Cole et al. 2011). With its primary seed disperser, the Shasta Ground Sloth, extinct, the species ability to shift into suitable habitat is limited (Cole et al. 2011).

Climatic conditions threaten the species in the short and long term, in multiple ways, through increased temperatures, drought, and precipitation timing. While this species is tolerant of drought, young plants including seedlings experience greater mortality and lower germination success during drought, which is increasing in severity currently and into the future due to climate change. Studies are needed to understand the impact of this threat and to document declines. The species range is expected to become more arid, specifically drier and hotter, with climate change. The species habitat is predicted to shrink and move into refugia, northward, and to higher elevations (USFWS 2018).

Habitat loss, including degradation of soil structure loss and loss of plant cover, is caused by development, military activities, grazing animals, renewable energy development, and off road vehicle use. About 0.7% of the species range is in areas with residential and urban development. Plants receive some protection by local ordinances (USFWS 2018). About 8.5% of the species range in on military lands, but the species is not believed to be impacted, and potentially benefit by management plans and conservation efforts (USFWS 2018). Around 53% of this species range is allocated for grazing allotments but not all are actively grazed. Grazing animals browse plants, including flowers below 2 meters in height, trample young plants, and contribute to a loss of soil structure that can degrade habitat (USFWS 2018, Lybbert and St. Clair 2017). Off road vehicle use can be severe where it occurs, causing mortality to this species and its nurse plants and damage to the seed bank and degradation to the soil structure (USFWS 2018).

An additional threat to the species is damage and mortality from native herbivores (USFWS 2018).
Ecology & Habitat

Habitat

This species is somewhat of a generalist of flats, gentle slopes, mesas, and bajadas on a variety of substrates, but typically igneous, that are silty, loamy, or sandy, within many different plant communities including Yellow Pine Forest and Sonoran Desert (USFWS 2019, Lenz 2007). The species has tolerance for saline and alkaline conditions, but does have a tendency to occur in areas with consistent precipitation year round, although of varying overall totals (USFWS 2019, Lenz 2007). It tolerates winter lows of 4 °C (39 °F) and summer highs of 46 °C (110 °F) (USFWS 2019).

Reproduction

In a study of Joshua Tree, seed caching rodents were found to cache seeds within 30 m of host plant (Wall et al. 2006). The presence of rhizomes allow for vegetative (asexual) spread of the species (USFWS 2018). Nurse plants are important for successful seedling survival by creating favorable microclimates and protection from herbivory (USFWS 2018).
Terrestrial Habitats
Forest/WoodlandWoodland - ConiferShrubland/chaparralDesert
Other Nations (1)
United StatesN3
ProvinceRankNative
NevadaS3Yes
CaliforniaSNRYes
UtahS1Yes
ArizonaS3Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)Serious or 31-70% pop. declineHigh (continuing)
1.1 - Housing & urban areasNegligible (<1%)Serious or 31-70% pop. declineHigh (continuing)
2 - Agriculture & aquacultureLarge (31-70%)Slight or 1-10% pop. declineHigh (continuing)
2.3 - Livestock farming & ranchingLarge (31-70%)Slight or 1-10% pop. declineHigh (continuing)
2.3.4 - Scale unknown/unrecordedLarge (31-70%)Slight or 1-10% pop. declineHigh (continuing)
3 - Energy production & miningSmall (1-10%)UnknownHigh (continuing)
3.3 - Renewable energySmall (1-10%)UnknownHigh (continuing)
6 - Human intrusions & disturbanceRestricted (11-30%)Moderate or 11-30% pop. declineHigh (continuing)
6.1 - Recreational activitiesRestricted (11-30%)Moderate or 11-30% pop. declineHigh (continuing)
6.2 - War, civil unrest & military exercisesSmall (1-10%)Neutral or Potential BenefitHigh (continuing)
7 - Natural system modificationsRestricted - smallSerious or 31-70% pop. declineHigh (continuing)
7.1 - Fire & fire suppressionRestricted - smallSerious or 31-70% pop. declineHigh (continuing)
7.1.1 - Increase in fire frequency/intensityRestricted - smallSerious or 31-70% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesRestricted (11-30%)Moderate or 11-30% pop. declineHigh (continuing)
8.2 - Problematic native species/diseasesRestricted (11-30%)Moderate or 11-30% pop. declineHigh (continuing)
8.2.1 - Unspecified speciesRestricted (11-30%)Moderate or 11-30% pop. declineHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh - low
11.1 - Habitat shifting & alterationPervasive (71-100%)UnknownHigh - low
11.2 - DroughtsPervasive (71-100%)UnknownHigh - moderate

Plant Characteristics
DurationPERENNIAL, Long-lived, EVERGREEN
Economic Value (Genus)No
Roadless Areas (15)
Nevada (11)
AreaForestAcres
Angel Peak NorthHumboldt-Toiyabe National Forest12,577
Angel Peak SouthHumboldt-Toiyabe National Forest6,540
Bald Mtn.Humboldt-Toiyabe National Forest41,598
Charleston - CarpenterHumboldt-Toiyabe National Forest17,828
Charleston - ClarkHumboldt-Toiyabe National Forest4,674
Charleston - Macks CynHumboldt-Toiyabe National Forest11,378
Charleston - McfarlandHumboldt-Toiyabe National Forest2,465
La Madre - TroutHumboldt-Toiyabe National Forest2,101
Lovell Summit SouthHumboldt-Toiyabe National Forest28,455
PotosiHumboldt-Toiyabe National Forest5,145
Stirling - Clark BHumboldt-Toiyabe National Forest741
South Dakota (1)
AreaForestAcres
Indian CreekBuffalo Gap National Grassland24,666
Utah (3)
AreaForestAcres
CottonwoodDixie National Forest6,754
Pine Valley MountainsDixie National Forest57,673
Signal PeakFishlake National Forest30,889
References (15)
  1. CCH2 Portal. 2021. Consortium of California Herbaria. Online. Available: https//:www.cch2.org/portal/index.php (accessed 2021).
  2. Cole, K.L., K. Ironside, J. Eischeid, G. Garfin, P.B. Duffy, and C. Toney. 2011. Past and ongoing shifts in Joshua tree distribution support future modeled range contraction. Ecological Applications 21(1):137–149.
  3. Cole, W.S., Jr., A.S. James, C.I. Smith. 2017. First Recorded Observations of Pollination and Oviposition Behavior in <i>Tegeticula antithetica</i> (Lepidoptera: Prodoxidae) Suggest a Functional Basis for Coevolution with Joshua Tree (<i>Yucca</i>) Hosts. Annals of the Entomological Society of America 110(4):390–397.
  4. Flora of North America Editorial Committee (FNA). 2002a. Flora of North America north of Mexico. Vol. 26. Magnoliophyta: Liliidae: Liliales and Orchidales. Oxford Univ. Press, New York. xxvi + 723 pp.
  5. iNaturalist. 2021. Online. Available: https://www.inaturalist.org (accessed 2021).
  6. Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
  7. Lenz, L.W. 2007a. Reassessment of <i>Yucca brevifolia</i> and recognition of <i>Y. jaegeriana </i>as a distinct species. ALISO 24(1): 97-104.
  8. Royer, A. M., M.A. Streisfeld, and C.I. Smith. 2016. Population genomics of divergence within an obligate pollination mutualism: Selection maintains differences between Joshua tree species. American Journal of Botany 103(10):1730–1741.
  9. Southwest Environmental Information Network (SEINet). 2021. Collections Databases. Online. Available: https://swbiodiversity.org/seinet/collections/index.php (accessed 2021).
  10. USDA, Natural Resources Conservation Service, PLANTS Database [USDA PLANTS]. http://plants.usda.gov/. Accessed 2015.
  11. U.S. Fish and Wildlife Service (USFWS). 2016. 90-Day Findings on 10 Petitions. Federal Register 81(178): 63160-63165.
  12. U.S. Fish and Wildlife Service (USFWS). 2018. Joshua Tree Status Assessment. U.S. Fish and Wildlife Service. 113 pp. + Appendices A–C.
  13. U.S. Fish and Wildlife Service (USFWS). 2019. 12-Month Findings on Petitions To List Eight Species as Endangered or Threatened Species. Federal Register 84(158): 41694-41699.
  14. U.S. Fish and Wildlife Service (USFWS). 2023. National Listing Workplan. Online. Available: https://www.fws.gov/project/national-listing-workplan
  15. U.S. Fish and Wildlife Service (USFWS). 2023. Petition Finding for Joshua Trees (Yucca brevifolia and Y. jaegeriana). Notification of finding. Federal Register 88(46): 14536-14560.