Quercus turbinella

Greene

Shrub Live Oak

G5Secure Found in 59 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Identity
Unique IDELEMENT_GLOBAL.2.144542
Element CodePDFAG05270
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderFagales
FamilyFagaceae
GenusQuercus
Other Common Names
Sonoran scrub oak (EN) Sonoran Scrub Oak (EN) Turbinella Live Oak (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
Formerly, California populations of what here is referred to as Quercus john-tuckeri have been included in the concept of Quercus turbinella. Q. john-tuckeri has subsessile fruit and noncordate leaf bases as opposed to the consistently pedunculate fruit and strongly cordate leaf bases of Q. turbinella. The two species seem to be no more closely related to each other than each might be to other southwestern oaks, and Q. john-tuckeri shares at least as many characteristics with Quercus berberidifolia as with Q. turbinella. Thus, treatment of these two taxa as varieties of the same species is inappropriate (Tucker, 1961; Flora of North America, 1993). Varieties of Quercus turbinella are now recognized at the species level (Kartesz' 1999 data). Quercus turbinella var. ajoensis is treated as Q. ajoensis, and Q. turbinella var. californica as Q. john-tuckeri.
Conservation Status
Review Date2010-11-22
Change Date1988-08-31
Edition Date2010-11-23
Edition AuthorsCordeiro, J.
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Rank Reasons
It occurs in the mountains of southwestern Colorado through southern Utah and Nevada to southern California and northern Mexico. It is considered relatively secure throughout its range although fossil evidence indicated in previously occurred much further north but climate change eliminated most northern populations so the species may be susceptible to climate changes today, as well. Also, frequency, intensity, and extent of late spring freezes, and intensity and extent of the "Arizona monsoon" appear to be the major factors controlling successful sexual reproduction.
Range Extent Comments
It occurs in the mountains of southwestern Colorado through southern Utah and Nevada to southern California and northern Mexico (Little, 1979; Tucker, 1961; Tirmenstein, 1999). It extends eastward to the northwestern portion of the Trans-Pecos region of western Texas (Little, 1979). Shrub live oak is most abundant in the chaparral of central Arizona (Cottam et al., 1959; Pase, 1969; Pond, 1961). Shrub live oak-Gambel oak hybrids have been reported hundreds of miles north of the present-day range of shrub live oak in parts of northern Utah and central Colorado (Cottam et al., 1959; Tucker et al., 1961). Macrofossil evidence suggests that shrub live oak migrated northward in the warmer altithermal (or hypsithermal) period during which the Arizona monsoon shifted (Cottam et al., 1959; Neilson and Wullstein, 1983). Later climatic shifts to cooler temperatures presumably eliminated shrub live oak from this northern area, but the more cold-hardy hybrids survived in some protected areas (Cottam et al., 1959).
Threat Impact Comments
Shrub live oak is drought tolerant and typically occupies drier and warmer sites than Gambel oak (Neilson and Wullstein, 1983; 1985). In the northern part of its range, shrub live oak often grows on warm, dry, southern exposures (Ffolliot and Thorud, 1974). Arizona chaparral is characterized by a biseasonal precipitation pattern with summer and winter precipitation and spring and fall droughts (Davis, 1870). Annual precipitation averages 16 to 25 inches (410-640 mm) (Ffolliot and Thorud, 1974). Shrub live oak is well adapted to survive fire (Tirmenstein, 1999). This oak typically sprouts vigorously from the root crown and rhizomes in response to fire or other types of disturbance (Davis and Pase, 1977; Pase, 1969; Saunier and Wagle, 1967; Wright et al., 1979). Postfire establishment by seed also occurs.
Ecology & Habitat

Habitat

Dry desert slopes, often in juniper and pinyon woodlands; 800-2000 m (Flora of North America, 1993). It grows in semiarid, lower elevation chaparral, pinyon-juniper (Pinus-Juniperus spp.), shrub deserts, oak woodlands, ponderosa pine (P. ponderosa) and riparian communities of the Southwest (Johnson, 1988; Tiedemann and Schmutz, 1967; Tucker, 1961; Welsh et al., 1987). It is a dominant shrub in Arizona chaparral and frequently comprises up to 50% of the shrub cover on these sites (Knipe et al., 1979; Pase, 1969). Soil: Shrub live oak grows well on dry hillsides and mesas and tolerates a wide range of soil types. Growth is best on sandy to clay loams. Soils are often slightly acidic (Davis and Pase, 1977). This oak is not restricted to deep soils and can grow on shallow, broken and fractured substrates (Davis and Pase, 1977; Saunier and Wagle, 1967). Soils are typically coarse-textured and poorly developed in shrub live oak chaparral (Ffolliott and Thorus, 1974).

Reproduction

Shrub live oak reproduces through both sexual and vegetative means.
Sexual reproduction: Shrub live oak produces small acorns which usually germinate and establish from late July through mid-September (Pase, 1969; Tucker et al., 1961). Acorn production is largely dependent on the amount of precipitation received during the previous winter (Pase, 1969). The vast majority of shrub live oak seedling mortality is apparently attributable to drought. Shrub live oak acorns are characterized by a short period of viability, and seedbanking is unlikely. Pase (1969) reports "there is probably a negligible carryover of seeds from 1 year to the next." Very few viable seeds remain 1 year after burial, due in large part to predation by insects, birds, and mammals.
Vegetative reproduction: Shrub live oak tends to increase more through rhizome sprouting than by seedling establishment (Pase, 1969; Saunier and Wagle, 1967). Shrub live oak sprouts vigorously after fire, application of herbicides, or mechanical treatment (Davis and Pase, 1977; Pase and Lindenmuth, 1971; Wright et al., 1979).
Shrub live oak flowers from April through June. In Ventura County, California, shrub live oak usually flowers in April (Tucker, 1972). In Utah, flowering begins by April and ends by May. Shrub live oak acorns mature by the summer or early fall. Acorns were present on shrub live oak from late August to early September at 1 Arizona site (Saunier and Wagle, 1967). Acorns often germinate during the summer rainy period, with germination and emergence occurring from late July to mid-September (Pase, 1969).
Other Nations (1)
United StatesN5
ProvinceRankNative
UtahSNRYes
CaliforniaS4Yes
New MexicoSNRYes
ArizonaSNRYes
TexasSNRYes
NevadaS3Yes
ColoradoS3Yes
OklahomaS1Yes
Plant Characteristics
Economic Value (Genus)No
Roadless Areas (59)
Arizona (32)
AreaForestAcres
Arnold MesaPrescott National Forest12,286
Ash CreekPrescott National Forest7,663
Black CanyonPrescott National Forest10,683
Black CrossTonto National Forest5,966
Blind Indian CreekPrescott National Forest26,847
BoulderTonto National Forest40,359
Burro CanyonKaibab National Forest19,928
Cherry CreekTonto National Forest11,371
Cimarron HillsCoconino National Forest5,303
GaliuroCoronado National Forest28,333
GoldfieldTonto National Forest15,257
Grief HillPrescott National Forest12,535
HackberryCoconino National Forest17,885
Hell HoleApache-Sitgreaves National Forests15,512
HellsgateTonto National Forest6,171
Horse MesaTonto National Forest9,146
Hot AirApache-Sitgreaves National Forests31,712
Lime CreekTonto National Forest42,568
Lower San FranciscoApache-Sitgreaves National Forests59,310
MazatzalTonto National Forest16,942
Middle Dragoon RoadlessCoronado National Forest10,543
Mitchell PeakApache-Sitgreaves National Forests35,398
Painted BluffsApache-Sitgreaves National Forests43,118
PinalenoCoronado National Forest130,920
Pine Mountain Wilderness ContiguousPrescott National Forest3,129
Pine Mountain Wilderness ContiguousTonto National Forest6,518
PipestemApache-Sitgreaves National Forests34,598
Red PointKaibab National Forest7,139
Santa TeresaCoronado National Forest8,929
Sierra Ancha Wilderness ContiguousTonto National Forest7,787
SunsetApache-Sitgreaves National Forests28,948
Upper Rincon RoadlessCoronado National Forest2,991
Nevada (1)
AreaForestAcres
PotosiHumboldt-Toiyabe National Forest5,145
New Mexico (18)
AreaForestAcres
Apache Kid ContiguousCibola National Forest67,542
Black CanyonSanta Fe National Forest1,922
CajaSanta Fe National Forest5,304
Contiguous To Black & Aldo Leopold WildernessGila National Forest111,883
Contiguous To Gila Wilderness & Primitive AreaGila National Forest79,049
Devils CreekGila National Forest89,916
Dry CreekGila National Forest26,719
Frisco BoxGila National Forest38,979
Gila BoxGila National Forest23,759
Hell HoleGila National Forest19,553
Last Chance CanyonLincoln National Forest8,934
Ortega PeakLincoln National Forest11,545
Poverty CreekGila National Forest8,770
Ryan HillCibola National Forest34,201
San JoseCibola National Forest16,950
Sawyers PeakGila National Forest59,743
Virgin CanyonSanta Fe National Forest6,068
Wahoo MountainGila National Forest23,122
Utah (8)
AreaForestAcres
Bull ValleyDixie National Forest10,911
Cave CanyonDixie National Forest5,657
Cedar BenchDixie National Forest8,915
CottonwoodDixie National Forest6,754
MogotsuDixie National Forest16,762
Moody WashDixie National Forest31,835
Pine Valley MountainsDixie National Forest57,673
Stoddard MountainDixie National Forest13,165
References (22)
  1. Cottam, W.P., J.M. Tucker, and R. Drobnick. 1959. Some clues to Great Basin postpluvial climates provided by oak distributions. Ecology 49(3):361-377.
  2. Davis, E.A. 1970. Propagation of shrub live oak from cuttings. Botanical Gazette 131(1):55-61.
  3. Davis, E.A. and C.P. Pase. 1977. Root system of shrub live oak: implication for water yield in Arizona chaparral. Journal of Soil and Water Conservation 32:174-180.
  4. Ffolliott, P.F. and D.B. Thorud. 1974. Vegetation for increased water yield in Arizona. University of Arizona Agricultural Experiment Station Technical Bulletin 215. 38 pp.
  5. Flora of North America Editorial Committee. 1993b. Flora of North America north of Mexico. Vol. 1. Introduction. Oxford Univ. Press, New York. 372 pp.
  6. Harper, K.T., F.J. Wagstaff, and L.M. Kunzler. 1985. Biology and management of the Gambel oak vegetative type: A literature review. General Technical Report INT-179. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, Utah. 31 pp.
  7. Johnsen, T.N., Jr. 1988. Conditions influencing Turbinella oak (<i>Quercus turbinella</i>) mortality from picloram or picloram 2,4-D. Weed Science 36:810-817.
  8. 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.
  9. Knipe, O.D., C.P. Pase, and R.S. Carmichael. 1979. Plants of the Arizona chapparal. General Technical Report RM-64, USDA Forest Service, Rocky Mountain Forest Range and Experiment Station, Fort Collins, Colorado. 54 pp.
  10. Little, E.L., Jr. 1979. Checklist of United States trees (native and naturalized). Agriculture Handbook No. 541. U.S. Forest Service, Washington, D.C. 375 pp.
  11. Neilson, R.P. and L.H. Wullstein. 1983. Biogeography of two southwest American oaks in relation to atmospheric dynamics. Journal of Biogeography 10:275-297.
  12. Neilson, R.P. and L.H. Wullstein. 1985. Comparative drought physiology and biogeography of <i>Quercus gambelii </i>and <i>Quercus turbinella</i>. The American Midland Naturalist 114(2):259-271.
  13. Pase, C.P. 1969. Survival of <i>Quercus turbinella</i> and <i>Q. emoryi</i> seedlings in an Arizona chaparral community. The Southwestern Naturalist 14(2):149-156.
  14. Pase, C.P. and A.W. Lindenmuth Jr. 1971. Effects of prescribed fire on vegetation and sediment in oak-mountain mahogany chaparral. Journal of Forestry 69:800-805.
  15. Pond, F.W. 1961. Basal cover and production of weeping lovegrass under varying amounts of shrub live oak crown cover. Journal of Range Management 14:335-337.
  16. Rowlands, P.G. 1993. Climate factors and the distribution of woodlands vegetation in the Southwest. The Southwestern Naturalist 38(3):185-197.
  17. Saunier, R.E. and R.F. Wagle. 1967. Factors affecting the distribution of shrub live oak (<i>Quercus turbinella</i> Greene). Ecology 48:35-41.
  18. Tiedemann, A.R. and E.M. Schmutz. 1966. Shrub control and reseeding effects on the oak chaparral of Arizona. Journal of Range Management 19:191-195.
  19. Tirmenstein, D. 1999. <i>Quercus turbinella</i>. In: Fire Effects Information System. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available online: http://www.fs.fed.us/database/feis/ (accessed 22 November 2010).
  20. Tucker, J. M. 1972. Hermaphroditic flowers in Californian oaks. Madrono 21(7):482-486.
  21. Tucker, J.M., W.P. Cottam, and R. Drobnick. 1961. Studies in the <i>Quercus undulata</i> complex. II. The contribution of <i>Q</i>uercus <i>turbinella</i>. American Journal of Botany 48(4):329-339.
  22. Wright, H.A., L.F. Neuenschwander, and C.M. Britton. 1979. The role and use of fire in sagebrush-grass and pinyon-juniper plant communities: A state-of-the-art review. General Technical Report INT-58, USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, Utah. 48 pp.