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Introductory

SPECIES: Ephedra nevadensis | Nevada Ephedra
ABBREVIATION : EPHNEV SYNONYMS : Ephedra aspera Engelm. ex S.Wats E. reedii Cory [10] SCS PLANT CODE : EPNE EPNEA EPNEN COMMON NAMES : Nevada ephedra Nevada jointfir gray ephedra Mormon tea TAXONOMY : The fully documented scientific name of Nevada ephedra is Ephedra nevadensis S. Wats. Varieties are [10]: Ephedra nevadensis var. nevadensis Ephedra nevadensis var. aspera (Engelm. ex S. Wats.) L. Benson LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : D. Tirmenstein, March 1987 LAST REVISED BY AND DATE : D. Tirmenstein, August 1990 AUTHORSHIP AND CITATION : Tirmenstein, D. 1990. Ephedra nevadensis. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Ephedra nevadensis | Nevada Ephedra
GENERAL DISTRIBUTION : Nevada ephedra occurs from Utah and Arizona through Nevada to Harney County, Oregon, and into southeastern California and Mexico [4,26]. It grows in the Mojave Desert of California and in the transition zone between the Mojave and the Great Basin [3]. ECOSYSTEMS : FRES29 Sagebrush FRES30 Desert shrub FRES36 Mountain grasslands FRES40 Desert grasslands STATES : AZ CA CO NV OR TX UT MEXICO ADMINISTRATIVE UNITS : DEVA GRCA GRBA JOTR LAME NABR ZION BLM PHYSIOGRAPHIC REGIONS : 5 Columbia Plateau 6 Upper Basin and Range 7 Lower Basin and Range 12 Colorado Plateau KUCHLER PLANT ASSOCIATIONS : K038 Great Basin sagebrush K039 Blackbrush K040 Saltbush - greasewood K041 Creosotebush K044 Creosotebush - tarbush K046 Desert: vegetation largely lacking K051 Wheatgrass - bluegrass K055 Sagebrush steppe K057 Galleta - three-awn shrubsteppe SAF COVER TYPES : NO-ENTRY SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Nevada ephedra is an indicator of edaphic or biotic climax in a number of sagebrush (Artemisia spp.)-grassland communities. It is described as codominant with big sagebrush (A. tridentata) and Indian ricegrass (Oryzopsis hymenoides) in the following Nevada vegetation typing: Vegetation and soils of the Churchill Canyon Watershed [2]

VALUE AND USE

SPECIES: Ephedra nevadensis | Nevada Ephedra
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Nevada ephedra is reportedly the most important forage species of all North American ephedra (Ephedra spp.) [26]. It provides valuable browse for mule deer, mountain sheep, and pronghorn [21,22,26]. Nevada ephedra may be heavily utilized on mule deer winter ranges, particularly during times of food shortages, but is often largely ignored during the summer months [26]. However, in Utah, Smith and Beale [21] observed that pronghorns consumed significant amounts during brief periods of the summer. Quail, cottontail rabbits, mule deer, and mountain sheep often feed on Nevada ephedra during critical drought periods [22]. Nevada ephedra provides food for all classes of domestic livestock. It is, however, considered poor quality forage for horses [15]. Throughout much of the Great Basin, this shrub is an important winter food source for sheep, goats, and cattle [5]. PALATABILITY : Nevada ephedra browse is at least moderately palatable to mule deer and to all classes of domestic livestock. Young stems are preferred over older, tougher foliage [22]. Seeds are palatable to a wide variety of small birds and mammals. Overall palatability of Nevada ephedra in Utah has been rated as follows [6]: Cattle fair Sheep fair Horses fair Pronghorn fair Elk poor Mule deer fair White-tailed deer ---- Small mammals good Small nongame birds fair Upland game birds fair Waterfowl poor NUTRITIONAL VALUE : Nevada ephedra browse is low in sodium and phosphorus. Specific nutrient content varies according to plant part, phenological development, and site characteristics [27]. Food value has been examined in detail [16,27]. Selected values are as follows [16,27]: Mature, aerial part Ca 5.81% Mg 1.28% P 0.50% date sampled percent dry weight P Na K Ca Mg Si Feb. 11 .06 .003 .25 2.43 .18 .04 March 17 .09 .007 .31 2.21 .30 .07 April 4 .12 .012 .86 2.65 .34 .12 May 21 .08 .007 1.80 1.02 .17 .05 June 19 .08 .006 2.26 1.41 .20 .04 July 29 .05 .008 1.45 1.72 .18 .05 Sept. 24 .04 .007 .91 2.37 .21 .10 Dec. 31 .07 .009 .61 2.37 .19 .11 date sampled ppm Zn Cu Fe Mn B Al Sr Be Feb. 11 23 14 101 77 14 82 82 45 March 17 19 10 142 136 12 134 97 24 April 4 17 5 143 149 22 167 67 30 May 21 20 20 186 13 18 145 50 11 June 19 21 14 161 17 12 149 66 12 July 29 24 12 248 26 9 184 91 13 Sept. 24 22 19 240 38 10 188 96 18 Dec. 31 27 14 121 47 16 152 52 33 COVER VALUE : Cover value of Nevada ephedra has been rated as follows in Utah (Dittberner and Olson 1983): Pronghorn fair Elk poor Mule deer poor White-tailed deer ---- Small mammals good Small nongame birds fair Upland game birds fair Waterfowl poor VALUE FOR REHABILITATION OF DISTURBED SITES : Nevada ephedra commonly forms dense, slowly spreading colonies [J. A. Young, pers. comm. 1987]. Growth and establishment characteristics make this shrub valuable for use on disturbed sites where it can aid in soil stabilization [17]. Plants establish readily from direct seeding, transplants, or cuttings [17,26]. Seedlings emerge in late winter or early spring following fall or winter plantings [18]. Nevada ephedra is well adapted to many basin big sagebrush (Artemisia tridentata ssp. tridentata), Wyoming sagebrush (A. tridentata ssp. wyomingensis), black sagebrush (A. nova), gray low sagebrush (A. arbuscula), northern desert shrub, pinyon-juniper, and salt desert communities [18,23]. Seedlings have been successfully planted onto semiarid reclaimed strip mines in southwestern Wyoming and elsewhere, with survival rates ranging from 12 percent to 94 percent [12,20]. Nevada ephedra seedlings are tolerant of extreme drought but may take 5 to 10 years to grow 2 feet (0.61 m) in height [18]. OTHER USES AND VALUES : Nevada ephedra is occasionally cultivated as an ornamental [4]. Many species of ephedra have historically been used to make beverages and as a remedy for coughs, headaches, cold, fever, and other ailments. Native Americans traditionally roasted and ate the seeds or added them to breads [26]. MANAGEMENT CONSIDERATIONS : Radiation: Studies conducted at the Nevada test site indicate that exposure of Nevada ephedra to radiation results in reduced growth, much-decreased fruit production, and poor germination [27]. Browse: Utilization of Nevada ephedra can be difficult to detect due to the manner in which the stems break off at joints [18].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Ephedra nevadensis | Nevada Ephedra
GENERAL BOTANICAL CHARACTERISTICS : Nevada ephedra is a coarse, erect, opposite-branched evergreen shrub which grows from 0.82 to 4.1 feet (0.25-1.25 m) in height [4,5]. Stout, spreading branches are olive to brownish green and nearly leafless [26]. Young stems are pale green and nearly smooth, whereas old stems, which may exceed 0.16 inch (4 mm) in thickness, are yellowish to gray with fissured bark [4]. Roots are typically deep and fibrous [22]. Individual plants are often connected by underground "stolons" which are produced as branches become covered with wind-blown sand or silt [27]. The leaves of Nevada ephedra have been reduced to small scales, and most photosynthesis takes place in the stems [24]. Nevada ephedra is primarily dioecious with small greenish-yellow flowers [5,22]. Ellipsoid staminate cones and single light-brown to yellowish-green ovulate cones are borne at the nodes of young branches [4]. Smooth brown seeds or "nutlets" of Nevada ephedra occur singly or in pairs [4,26]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Seed: Nevada ephedra produces large quantities of small, smooth brown seeds at erratic intervals [4,27]. An abundance of seed is produced in some years but very little in others [18]. Germination occurs over a wide range of temperatures [31]. In laboratory tests, good germination was achieved at constant temperatures of 41 to 68 degrees F (5-20 degrees C), and at alternating exposure of 16 hours at 68 degrees F (20 degrees C) followed by 2 hours at 77 degrees F (25 degrees C) [31]. Germination is rapid under favorable conditions and can begin within 2 days. In laboratory tests, germination was 68 percent completed within 10 days after initial plantings [31]. However, at 41 degrees (5 degrees C), germination did not begin until the 7th day after planting and was only 36 percent complete after 14 days [31]. Seed has remained viable for up to 5 years in storage [4,18]. However, germination may be significantly reduced in seeds stored for only 1 year [31]. Seeds commonly germinate from the underground caches of rodents such as ground squirrels [R. Hunter, pers. comm. 1981]. Vegetative regeneration: Nevada ephedra sprouts from roots or woody crowns after fire and other disturbances [30]. New plants commonly develop from the roots or "stolons" of older clones in the absence of disturbance [27]. Seedling establishment: Seedlings are very tolerant of drought and generally establish well following fall or winter plantings [18,22]. SITE CHARACTERISTICS : Nevada ephedra is adapted to range of environmental conditions [3] but typically grows on arid hills and plains [27]. It occurs on dry, open slopes, ridges, breaks with southern exposures, canyons, floodplains, arroyos, and in dry watercourses [5,22]. Nevada ephedra grows well on gravelly or rocky, often alkaline soils and is tolerant of salt [5,17,22]. Most sites are well drained or subirrigated [5]. Nevada ephedra typically reaches greatest abundance at the edge of the salt desert zone [J. A. Young, pers. comm. 1987] but also occurs in basin big sagebrush, Wyoming sagebrush, gray low sagebrush, and black sagebrush communities. It generally grows as scattered plants or in small clumps but also occurs in isolated, large, pure stands [22]. Plants commonly growing with Nevada ephedra include grama (Bouteloua spp.), mountain-mahogany (Cercocarpus spp.), saltbush (Atriplex spp.), juniper (Juniperus spp.), creosotebush (Larrea spp.), and cholla (Opuntia spp.) [3,22]. Nevada ephedra typically grows below the elevational range of the closely related green ephedra (Ephedra viridis) [J. A. Young, pers. comm. 1987]. In Utah, it grows from 4,000 to 6,000 feet (1,220-1,830 m) [6]. SUCCESSIONAL STATUS : NO-ENTRY SEASONAL DEVELOPMENT : Plants generally flower from April to June, and fruit ripens in July [5,22,25]. However, significant annual variation in phenological development has been observed [25]. Flowering and fruiting dates were documented as follows in a 9-year study in southern Nevada [25]: year first flowering first fruiting 1968 February 9 April 10 1969 April 25 May 2 1970 None None 1971 March 21 April 15 1972 March 18 March 27 1973 April 18 May 7 1974 April 25 None 1975 April 29 May 21 1976 April 9 None On harsh sites, plants may exhibit very little vegetative growth, even during favorable years [27].

FIRE ECOLOGY

SPECIES: Ephedra nevadensis | Nevada Ephedra
FIRE ECOLOGY OR ADAPTATIONS : Nevada ephedra generally sprouts from the root or crown after fire damages or destroys aboveground vegetation [27,28,29]. However, under certain circumstances, regenerative structures may be eliminated by hot fires [14,32]. Nevada ephedra may also reoccupy disturbed sites through seed. Under laboratory conditions, seed has remained viable for up to 5 years [18], and postfire germination of on-site seed is possible. Small birds and mammals may transport some seed to burned areas. Fires may not carry on some Nevada ephedra sites due to insufficient fuels. Periods of above normal precipitation can contribute to increased stand flammability by promoting the growth of annuals [14]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown

FIRE EFFECTS

SPECIES: Ephedra nevadensis | Nevada Ephedra
IMMEDIATE FIRE EFFECT ON PLANT : Underground regenerative structures commonly survive when aboveground vegetation is consumed by fire [28]. However, under certain circumstances, plants may be killed [22,32]. The effects of fire on Nevada ephedra varies according to fire intensity and severity, and season of burn. Following a hot June wildfire, aboveground foliage was killed on 84 percent of Nevada ephedra at this site. Approximately 76 percent of all plants were completely killed [14]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Nevada ephedra often sprouts vigorously from the roots after aboveground vegetation is killed or damaged by fire [28]. Recovery is generally rapid when plants sprout prolifically. In a central Utah study, significant amounts of Nevada ephedra were present within 1 year after fire [28]. However, response may vary according to the timing, intensity, and severity of burn. Only 9 percent of all top-killed plants sprouted after a hot June wildfire in the Sonoran Desert of Arizona [14]. Nevada ephedra can sometimes reoccupy a site through seed, but recovery may be relatively slow. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Nevada ephedra sprouted readily after a mid-summer wildfire in central Utah. Coverage values and biomass was documented as follows [28]: Measured Preburn Control (Unburned) Burned (percent) 1981 1982 1983 1981 1982 1983 1981 1982 1983 2.5 2.5 2.3 1.0 4.3 2.0 -- 1.3 1.0 Means (kg/ha) - herbage standing crops 1981 1982 1983 23.98 10.18 95.01 Little sprouting occurred after a hot June wildfire in Arizona. Density and cover on burned and unburned plots were as follows [14]: unburned burned 1980 1981 density (#/ha) 40 -- 5 cover (%) 0.9 -- trace FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Ephedra nevadensis | Nevada Ephedra
REFERENCES : 1. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434] 2. Blackburn, Wilbert H.; Tueller, Paul T.; Eckert, Richard E., Jr. 1969. Vegetation and soils of the Churchill Canyon Watershed. R-45. Reno, NV: University of Nevada, Agricultural Experiment Station. 155 p. In cooperation with: U.S. Department of the Interior, Bureau of Land Management. [460] 3. Brotherson, Jack D.; Masslich, William J. 1985. Vegetation patterns in relation to slope position in the Castle Cliffs area of southern Utah. Great Basin Naturalist. 45(3): 535-541. [528] 4. Cronquist, Arthur; Holmgren, Arthur H.; Holmgren, Noel H.; Reveal, James L. 1972. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 1. New York: Hafner Publishing Company, Inc. 270 p. [717] 5. Dayton, William A. 1931. Important western browse plants. Misc. Publ. 101. Washington, DC: U.S. Department of Agriculture. 214 p. [768] 6. Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information network (PIN) data base: Colorado, Montana, North Dakota, Utah, and Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 786 p. [806] 7. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 8. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others]. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998] 9. Holmgren, Arthur H.; Reveal, James L. 1966. Checklist of the vascular plants of the Intermountain Region. Res. Pap. INT-32. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 160 p. [1184] 10. Kartesz, John T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II--thesaurus. 2nd ed. Portland, OR: Timber Press. 816 p. [23878] 11. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation of the conterminous United States. Special Publication No. 36. New York: American Geographical Society. 77 p. [1384] 12. Luke, Forrest; Monsen, Stephen B. 1984. Methods and costs for establishing shrubs on mined lands in southwestern Wyoming. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 286-291. [1485] 13. Lyon, L. Jack; Stickney, Peter F. 1976. Early vegetal succession following large northern Rocky Mountain wildfires. In: Proceedings, Tall Timbers fire ecology conference and Intermountain Fire Research Council fire and land management symposium; 1974 October 8-10; Missoula, MT. No. 14. Tallahassee, FL: Tall Timbers Research Station: 355-373. [1496] 14. McLaughlin, Steven P.; Bowers, Janice E. 1982. Effects of wildfire on a Sonoran Desert plant community. Ecology. 63(1): 246-248. [1619] 15. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 342 p. [1702] 16. National Academy of Sciences. 1971. Atlas of nutritional data on United States and Canadian feeds. Washington, DC: National Academy of Sciences. 772 p. [1731] 17. Plummer, A. Perry. 1977. Revegetation of disturbed Intermountain area sites. In: Thames, J. C., ed. Reclamation and use of disturbed lands of the Southwest. Tucson, AZ: University of Arizona Press: 302-337. [171] 18. Plummer, A. Perry; Christensen, Donald R.; Monsen, Stephen B. 1968. Restoring big-game range in Utah. Publ. No. 68-3. Ephraim, UT: Utah Division of Fish and Game. 183 p. [4554] 19. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 20. Shaw, Nancy; Monsen, Stephen B. 1984. Nursery propagation and outplanting of bareroot Chenopod seedlings. In: Tiedemann, Arthur R.; McArthur, E. Durant; Stutz, Howard C.; [and others], compilers. Proceedings--symposium on the biology of Atriplex and related chenopods; 1983 May 2-6; Provo, UT. Gen. Tech. Rep. INT-172. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 251-260. [2123] 21. Smith, Arthur D.; Beale, Donald M. 1980. Pronghorn antelope in Utah: some research and observations. Publication No. 80-13. Salt Lake City, UT: Utah Division of Wildlife Resources. 88 p. [5305] 22. Stanton, Frank. 1974. Wildlife guidelines for range fire rehabilitation. Tech. Note 6712. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 90 p. [2221] 23. Stevens, Richard. 1983. Species adapted for seeding mountain brush, big, black, and low sagebrush, and pinyon-juniper communities. In: Monsen, Stephen B.; Shaw, Nancy, compilers. Managing Intermountain rangelands--improvement of range and wildlife habitats: Proceedings; 1981 September 15-17; Twin Falls, ID; 1982 June 22-24; Elko, NV. Gen. Tech. Rep. INT-157. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 78-82. [2240] 24. Strojan, Carl L.; Turner, Frederick B.; Castetter, Richard. 1979. Litter fall from shrubs in the northern Mojave Desert. Ecology. 60(5): 891-900. [2266] 25. Turner, Frederick B.; Randall, David C. 1987. The phenology of desert shrubs in southern Nevada. Journal of Arid Environments. 13: 119-128. [2764] 26. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 27. Wallace, A.; Romney, E. M. 1972. Radioecology and ecophysiology of desert plants at the Nevada Test Site. Rep. TID-25954. [Washington, DC]: U.S. Atomic Energy Commission, Office of Information Services. 439 p. [15000] 28. West, Neil E.; Hassan, M. A. 1985. Recovery of sagebrush-grass vegetation following wildfire. Journal of Range Management. 38(2): 131-134. [2513] 29. Young, James A.; Evans, Raymond A. 1973. Downy brome--intruder in the plant succession of big sagebrush communities in the Great Basin. Journal of Range Management. 26(6): 410-415. [2651] 30. Young, James A.; Evans, Raymond A. 1978. Population dynamics after wildfires in sagebrush grasslands. Journal of Range Management. 31(4): 283-289. [2657] 31. Young, James A.; Evans, Raymond A.; Kay, Burgess L. 1977. Ephedra seed germination. Agronomy Journal. 69: 209-211. [6237] 32. Wright, Henry A. 1980. The role and use of fire in the semidesert grass-shrub type. Gen. Tech. Rep. INT-85. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 24 p. [2616] 33. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090] 34. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. [23362] 35. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. [23104] 36. U.S. Department of the Interior, National Biological Survey. [n.d.]. NP Flora [Data base]. Davis, CA: U.S. Department of the Interior, National Biological Survey. [23119]

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