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Introductory

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
ABBREVIATION : ARTPYG SYNONYMS : NO-ENTRY SCS PLANT CODE : NO-ENTRY COMMON NAMES : pygmy sagebrush pigmy sagebrush TAXONOMY : The fully documented scientific name of pygmy sagebrush is Artemisia pygmaea A.Gray [9]. Pygmy sagebrush was formerly placed in the monotypic section Pygmaeae by Rydberg (1916) [1]. Many later researchers, including Beetle [1] and Ward [22], grouped Artemisia pygmaea into the section Tridentatae. According to McArthur [12], karyotype, stem anatomy, and chromatography all suggest an affinity with the section Tridentatae. This unique species is, however, considered by many to be difficult to place taxonomically [12,18]. Possible origins of pygmy sagebrush are also unclear. Beetle [1] maintains that pygmy sagebrush has more features in common with black sagebrush (Artemisia nova) and may have diverged from this stalk long ago. Other researchers believe that a prototype of the Tridentatae line may have given rise to pygmy sagebrush [2,22]. According to Beetle [1], pygmy sagebrush is one of the most uniform types in Tridentatae and shows little evidence of hybridizing with other species. Both diploid and tetraploid forms occur [13]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : NO-ENTRY OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : D. Tirmenstein June, 1987. LAST REVISED BY AND DATE : D. Tirmenstein January, 1988. AUTHORSHIP AND CITATION : Tirmenstein, D. 1987. Artemisia pygmaea. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
GENERAL DISTRIBUTION : Pygmy sagebrush occurs from northern Arizona throughout the Great Basin of Nevada and Utah and the Uinta Basin of Utah and Colorado [18]. It is uncommon, but locally abundant, throughout its range [22] and covers approximately 21 square miles (5,000 ha) [13]. ECOSYSTEMS : FRES29 Sagebrush FRES30 Desert shrub FRES35 Pinyon - juniper STATES : AZ CO NV UT ADMINISTRATIVE UNITS : BRCA GRCA BLM PHYSIOGRAPHIC REGIONS : 6 Upper Basin and Range 7 Lower Basin and Range 10 Wyoming Basin 12 Colorado Plateau KUCHLER PLANT ASSOCIATIONS : K023 Juniper - pinyon woodland K040 Saltbush - greasewood K057 Galleta - three awn shrubsteppe SAF COVER TYPES : 239 Pinyon - juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Pygmy sagebrush grows in desert grassland, pinyon-juniper, and salt desert shrub communities of the Great Basin and Uinta Basin. At some mesic, less saline, salt desert sites, pygmy sagebrush, black sagebrush (Artemisia nova) and/or budsage (Artemisia spinescens) dominate the plant community [23]. Pygmy sagebrush has not been described as an indicator of climax.

VALUE AND USE

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Pygmy sagebrush is small and relatively scarce and consequently provides little forage for livestock or wildlife [13]. PALATABILITY : In some areas of Utah, mule deer use of pygmy sagebrush is described as moderate [16]. However, Brunner [4] reported that pygmy sagebrush was rarely browsed in the Great Basin of Nevada. The overall value of pygmy sagebrush as browse is probably low [10]. The palatability and degree of use by livestock and wildlife species for pygmy sagebrush in Utah is as follows [5]: Cattle Poor Sheep Fair Horses Poor Pronghorn Fair Elk Poor Mule Deer Poor Small mammals Fair Small nongame birds Poor Upland game birds Fair Waterfowl Poor NUTRITIONAL VALUE : Pygmy sagebrush is rated as poor in both energy and protein value [5]. Average utilization by mule deer and relative concentrations of three major volatile compounds from a Utah study are as follows [16]: utilization methacrolein alpha-pinene arthole 54% 0.35% 28.42% 1.62% COVER VALUE : Pygmy sagebrush provides little cover for larger species of wildife due to its dwarf, cushionlike growth form. The degree to which pygmy sagebrush provides environmental protection during one or more seasons for wildlife species in Utah is as follows [5]: Pronghorn Poor Elk Poor Mule deer Poor Small mammals Fair Small nongame birds Poor Upland game birds Poor Waterfowl Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Some researchers report that pygmy sagebrush has low value for erosion control and for long- and short-term revegetation [5]. Others claim that this species has good potential for soil stabilization and is at least moderately adapted for growth on many types of disturbed sites [14]. Although pygmy sagebrush spreads well from naturally dispersed seed, artificial plantings have been unsuccessful [13]. Seed preparation is apparently difficult, and seed handling characteristics are poor [14]. Individual plants can be divided and successfully transplanted onto disturbed sites [13,14]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Pygmy sagebrush provides a valuable ground cover on dry alkaline sites where few other plants can survive [13].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
GENERAL BOTANICAL CHARACTERISTICS : Pygmy sagebrush is a dwarf, depressed, perennial cushionlike evergreen shrub or half-shrub which grows up to 8 inches (2 dm) in height [1,13]. Both diploid and tetraploid forms occur [13]. This desert species exhibits numerous morphological adaptations which enable it to survive on extremely xeric sites. Leaves are green, glabrous, and pinnately divided into 3 to 11 lobes [22]. The numerous stomates are sunken, and water vessels are extremely narrow which facilitates water conservation [17]. The bark of older branches is brown and fibrous, whereas younger branches are straw-colored and puberulent [22]. Heads made up of three- to five-toothed disk flowers are arranged in a spikelike inflorescence [1,13]. Ray flowers are lacking [13]. RAUNKIAER LIFE FORM : Chamaephyte REGENERATION PROCESSES : Pygmy sagebrush regenerates readily from seed which matures in October [13]. Seed is large for the genus Artemisia and averages 440,000 per lb (970 per g) [13]. Pygmy sagebrush generally spreads well from naturally dispersed seed, although artificial seeding has to date been largely unsuccessful [13]. Pygmy sagebrush does not resprout after fire or other disturbance [1,21]. It does, however, establish readily when individual plants are divided and transplanted [13]. Information on seed dispersal mechanisms, germination, and establishment is lacking. Beetle [1] noted that seedlings of pygmy sagebrush are "unknown." SITE CHARACTERISTICS : Widely disjunct populations of pygmy sagebrush grow on calcareous desert soils of the Great Basin and Uinta Basin [1,12]. Pygmy sagebrush occurs on shale barrens at lower elevations [18] and has also been reported on white gypsum outcrops in the Great Basin of Nevada [4]. It grows in pinyon-juniper communities of Utah [8] and at more mesic sites in the salt desert shrub zone with black sagebrush and budsage [23]. In Nevada it is most often associated with the halophytic threadleaf rubber rabbitbrush (Chrysothamnus nauseosus ssp. consimilis) and in Utah has been reported to occur in large stands with black sagebrush [13]. Pygmy sagebrush often grows in association with other cushion-formers [22], many of which are rare or narrowly endemic [8]. It typically occurs extremely xeric sites [17]. Growth on sandy loam, loam, and clay loam is described as "good" [14]. Pygmy sagebrush also grows well on alkaline soils [14]. Optimum soil depth is 10 to 20 inches (25-51 cm) [5]. Pygmy sagebrush grows from 4,000 to 6,000 feet (1,220-1,830 m) throughout its range [10]. It ocurs from 5,300 to 6,000 feet (1,617-1,830 m) in Utah [8]. SUCCESSIONAL STATUS : NO-ENTRY SEASONAL DEVELOPMENT : Pygmy sagebrush flowers during August and September. Seed matures in October [13].

FIRE ECOLOGY

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
FIRE ECOLOGY OR ADAPTATIONS : Pygmy sagebrush is killed by fire but readily reoccupies a site through seed [1]. It does not resprout following fire or other disturbance [1,21]. POSTFIRE REGENERATION STRATEGY : Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
IMMEDIATE FIRE EFFECT ON PLANT : Pygmy sagebrush is killed by most fires [1]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Pygmy sagebrush does not sprout after aboveground vegetation is killed by fire [1,21]. It does however, reseed readily following fire [1]. Pygmy sagebrush is reported to spread well from naturally dispersed seed [13]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Artemisia pygmaea | Pygmy Sagebrush
REFERENCES : 1. Beetle, A. A. 1960. A study of sagebrush: The section Tridentatae of Artemisia. Bulletin 368. Laramie, WY: University of Wyoming, Agricultural Experiment Station. 83 p. [416] 2. Beetle, Alan A.; Johnson, Kendall L. 1982. Sagebrush in Wyoming. Bull. 779. Laramie, WY: University of Wyoming, Agricultural Experiment Station. 68 p. [421] 3. 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] 4. Brunner, James R. 1972. Observations on Artemisia in Nevada. Journal of Range Management. 25: 205-298. [550] 5. 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] 6. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 7. 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] 8. Goodrich, Sherel; Neese, Elizabeth. 1986. Uinta Basin flora. [Place of publication unknown]: U.S. Department of Agriculture, Forest Service. 320 p. [23307] 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. Johnson, Kendall L. 1987. Sagebrush types as ecological indicators to integrated pest management (IPM) in the sagebrush ecosystem of western North America. In: Onsager, Jerome A., ed. Integrated pest management on rangeland: State of the art in the sagebrush ecosystem. ARS-50. Washington, DC: U.S. Department of Agriculture, Agricultural Research Service: 1-10. [2841] 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. McArthur, E. Durant. 1983. Taxonomy, origin and distribution of big sagebrush ( Artemisia tridentata) and allies (subgenus Tridentatae). In: Johnson, Kendall L., ed. Proceedings--first Utah shrub ecology workshop; 1981 September 9-10; Ephraim, UT. Logan, UT: Utah State University: 3-14. [1566] 13. McArthur, E. Durant; Blauer, A. Clyde; Plummer, A. Perry; Stevens, Richard. 1979. Characteristics and hybridization of important Intermountain shrubs. III. Sunflower family. Res. Pap. INT-220. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 82 p. [1571] 14. 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] 15. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 16. Scholl, Jackson P.; Kelsey, Rick G.; Shafizadeh, Fred. 1977. Involvement of volatile compounds of Artemisia in browse preference by mule deer. Biochemical Systematics and Ecology. 5: 291-295. [2086] 17. Shultz, Leila M. 1986. Comparative leaf anatomy of sagebrush: ecological considerations. In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 253-264. [2140] 18. Shultz, Leila M. 1986. Taxonomic and geographic limits of Artemisia subgenus tridentatae (Beetle). In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 20-28. [2141] 19. 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] 20. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of scientific plant names. Vol. 1. List of plant names. SCS-TP-159. Washington, DC. 416 p. [11573] 21. Walton, Todd P.; White, Richard S.; Wambolt, Carl L. 1986. Artemisia reproductive strategies: a review with emphasis on plains silver sagebrush. In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 67-74. [2447] 22. Ward, George H. 1953. Artemisia, section Seriphidium, in North America: a cytotaxonomic study. Contributions from the Dudley Herberium. Stanford, CA: Stanford University, Natural History Museum; 4(6): 155-205. [2454] 23. West, Neil E. 1979. Basic synecological relationships of sagebrush-dominated lands in the Great Basin and the Colorado Plateau. In: The sagebrush ecosystem: a symposium: Proceedings; 1978 April; Logan, UT. Logan, UT: Utah State University, College of Natural Resources; 1979: 33-41. [2502]

Index

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