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Introductory

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
ABBREVIATION : ARTARBT SYNONYMS : NO-ENTRY SCS PLANT CODE : ARART COMMON NAMES : hotsprings sagebrush cleftleaf sagebrush thermopola sagebrush thermopola low sagebrush TAXONOMY : The currently accepted scientific name of hotsprings sagebrush is Artemisia arbuscula Nutt. ssp. thermopola Beetle. There are two other subspecies of low sagebrush (A. arbuscula): A. arbuscula ssp. arbuscula (gray low sagebrush) and A. arbuscula ssp. longiloba (Osterhout) L. Shultz (alkali sagebrush) [35,36]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : NO-ENTRY OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : D. Tirmenstein, September, 1986. LAST REVISED BY AND DATE : D. Tirmenstein, September 1988 AUTHORSHIP AND CITATION : Tirmenstein, D. 1988. Artemisia arbuscula ssp. thermopola. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
GENERAL DISTRIBUTION : Hotsprings sagebrush occurs in east-central Oregon, the Stanley Basin of Idaho, and near Jackson, Wyoming, along the Wyoming-Idaho-Utah borders [19]. It grows on harsh sites in both Yellowstone and Grand Teton National Parks [2]. ECOSYSTEMS : FRES21 Ponderosa pine FRES26 Lodgepole pine FRES29 Sagebrush FRES34 Chaparral - mountain shrub STATES : ID OR UT WY ADMINISTRATIVE UNITS : GRTE YELL BLM PHYSIOGRAPHIC REGIONS : 5 Columbia Plateau 8 Northern Rocky Mountains 9 Middle Rocky Mountains KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K012 Douglas-fir forest K037 Mountain mahogany - oak scrub K055 Sagebrush steppe SAF COVER TYPES : 210 Interior Douglas-fir 218 Lodgepole pine 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Hotsprings sagebrush occurs as a dominant in sagebrush-grassland communities in Yellowstone and Grand Teton National Parks and elsewhere within its range. It is listed as a codominant indicator species along with Idaho fescue (Festuca idahoensis) in the following publications: Sagebrush-grass habitat types of southern Idaho [14] A preliminary description of plant communities found on the Sawtooth, White Cloud, Boulder, and Pioneer Mountains [22] Hotsprings sagebrush frequently grows in mosaics with big sagebrush and is commonly associated with Idaho fescue [19,30]. Plant associates and habitat requirements are similar to the more widely distributed gray low sagebrush [30]. Common plant associates include fernleaf fleabane (Erigeron compositus), rosey pussytoes (Antennaria rosea), Hood's phlox (Phlox hoodii), chimaya (Cymopterus bipinnatus), aster (Aster ssp.), and sulfur erigogonum (Eriogonum umbellatum) [22]. Some authorities believe that hotsprings sagebrush is restricted to areas adjacent to those occupied by threetip sagebrush (Artemisia tripartita) and gray low sagebrush [25].

VALUE AND USE

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Comparatively little is known about the importance of hotsprings sagebrush to livestock and wildlife. Low sagebrush (Artemisia arbulsula) is considered a valuable browse plant at some locations during the spring, fall, and winter months [16]. Mule deer, pronghorn, bighorn sheep, and sage grouse all utilize the closely related gray low sagebrush [5,24]. Domestic sheep and, to a much lesser degree, cattle consume gray low sagebrush, particularly during the spring, fall, and winter [8,24]. Gray low sagebrush provides little winter forage in many parts of its range because of extreme snow depths [3]. Hotsprings sagebrush occurs on higher and colder sites than gray low sagebrush, and winter utilization of this species may be even more limited. PALATABILITY : The palatability of hotsprings sagebrush to livestock and wildlife is rated low to moderate [3]. It provides some winter forage, but is largely ignored during the summer months [3]. NUTRITIONAL VALUE : Energy and protein values of low sagebrush are rated fair [10]. Crude protein, fat, and fiber contents of hotsprings sagebrush leaves and stems are 6.40 percent, 4.40 percent, and 34.54 percent, respectively [2]. COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Removing hotsprings sagebrush to increase herbage production on some sites has been recommended [15]. Best results have been obtained on sites with at least remnant bunchgrass populations [30]. However, other researchers recommend against treating low sagebrush communities, citing minimal improvement or even further deterioration [2].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
GENERAL BOTANICAL CHARACTERISTICS : Hotsprings sagebrush is a dwarf, spreading shrub reaching 12 inches (3 dm) in height, with a crown spread of 12 to 16 inches (30-40 cm) [2]. It closely resembles the more widespread subspecies gray low sagebrush in morphology. However, leaves are more finely divided than those of gray low sagebrush and have three long, linear divisions [2,25]. Numerous vegetative branches are present. Culms are 4 to 12 inches (10-30 cm) long [2]. Hotsprings sagebrush is resistant to drought [26]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Hotsprings sagebrush reproduces only through light, wind-dispersed seed [2]. Very little is known about germination rates or requirements. SITE CHARACTERISTICS : Hotsprings sagebrush typically occurs on dry, shallow, infertile and rocky ridgetops or benches [14,22]. It grows well in the cold, dry mountain valleys of central and eastern Idaho, northern Utah, and northeastern Wyoming [22,23]. Hotsprings sagebrush dominates extensive, nearly uniform communities in many areas including parts of Yellowstone and Grand Teton National Parks [3], but also grows in openings in lodgepole pine (Pinus contorta) or ponderosa pine (P. ponderosa) forests [2,30]. Many authorities believe that the distribution of low sagebrush is largely related to soil conditions. Hotsprings sagebrush generally grows on poorly drained soils with a high clay content. Soils are generally less than 13 inches (33 cm) to an impermeable B horizon or, if deeper, with 30 percent or more gravel and cobbles in the horizon [28]. Growth has been reported on volcanics, sediments, and granitics [22]. In central Idaho hotsprings sagebrush grows on glacial outwash, dry alluvium, terraces, or on poorly drained mountainous sites [22]. Soils which support hotsprings sagebrush tend to be drier and rockier than those which support big sagebrush (Artemisia tridentata) [3]. Hotsprings sagebrush typically grows on higher and cooler sites than the closely related gray low sagebrush [14]. Hotsprings sagebrush sites are characterized by large amounts of bare soil and exposed rock. Hotsprings sagebrush grows on all aspects on slopes of 10 to 15 percent or less [22]. Hotsprings sagebrush typically grows above 6,000 feet (1,829 m) [23]. Elevational ranges are as follows [2,22,30]: from 6,000 to 9,800 ft (1,830 to 2,989 m) in ID 5,000 to 9,000 ft (1,524 to 2,743 m) in OR 6,000 to 7,000 ft (1,829 to 2,134 m) in WY SUCCESSIONAL STATUS : Hotsprings sagebrush occurs with Idaho fescue in a number of low sagebrush-bunchgrass climax communities [14,22]. Climax conditions in these communities are generally attributable to edaphic factors. Hotsprings sagebrush also occurs as a dominant in uniform, climax populations in northwestern Wyoming and eastern Idaho and is also represented in some early seral communities. SEASONAL DEVELOPMENT : Seasonal development of hotsprings sagebrush is poorly known. Some researchers believe that its phenology is similar to that of gray low sagebrush [2], while others maintain that hotsprings sagebrush exhibits earlier phenological development [19]. Shultz [25] reports that hotsprings sagebrush blooms in late summer and fall. Seed matures from late August through October, and ripens by October or November [2,30].

FIRE ECOLOGY

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
FIRE ECOLOGY OR ADAPTATIONS : Evidence suggests that hotsprings sagebrush is readily killed by fire. It is not known to sprout, but reestablishes through light, off-site, wind-dispersed seed from surviving plants adjacent to the burn. Low sagebrush communities are characterized by a depauperate understory with much exposed soil and surface rock. Many stands lack sufficient fuels to carry a fire [1,5,7]. Consequently, fires in hotsprings sagebrush communities are probably rare. The probability of fire increases as herbaceous growth increases as a result of above-average precipitation or increased protection from grazing [7]. Weedy species such as medusahead (Taeniatherum caput-medusae) and cheatgrass (Bromus tectorum) will increase flammability of low sagebrush stands [7,33]. POSTFIRE REGENERATION STRATEGY : Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
IMMEDIATE FIRE EFFECT ON PLANT : Hotsprings sagebrush is propbably killed outright by fire. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Hotsprings sagebrush probably colonizes a burn through small, light, wind-dispersed seed from off-site plants. Response time is not well documented. Gray low sagebrush responds variably, with recovery described as "slow to rapid" [34]. Gray low sagebrush can recover within 2 to 5 years with favorable conditions, but more than 10 years may be required under less favorable circumstances [34]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Fires are rare in low sagebrush communities due to lack of fuel. Fires do not carry in communities dominated by gray low sagebrush even on hot days with winds up to 25 miles per hour (40 km/hr) [1,6]. Gray low sagebrush has been successfully used as a fuelbreak when adjacent big sagebrush communities have been burned [32,34]. Prescribed fires may not be possible or desirable in hotsprings sagebrush stands. Fires in most low sagebrush communities produce relatively few benefits [1,7,34].

REFERENCES

SPECIES: Artemisia arbuscula ssp. thermopola | Hotsprings Sagebrush
REFERENCES : 1. Beardall, Louis E.; Sylvester, Vern E. 1976. Spring burning for removal of sagebrush competition in Nevada. In: Proceedings, Tall Timbers fire ecology conference and fire and land management symposium; 1974 October 8-10; Missoula, MT. No. 14. Tallahassee, FL: Tall Timbers Research Station: 539-547. [406] 2. 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] 3. Beetle, Alan A.; Johnson, Kendall L. 1982. Sagebrush in Wyoming. Bull. 779. Laramie, WY: University of Wyoming, Agricultural Experiment Station. 68 p. [421] 4. 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] 5. Blaisdell, James P.; Murray, Robert B.; McArthur, E. Durant. 1982. Managing Intermountain rangelands--sagebrush-grass ranges. Gen. Tech. Rep. INT-134. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 41 p. [467] 6. Britton, Carlton M.; Ralphs, Michael H. 1979. Use of fire as a management tool in sagebrush ecosystems. In: The sagebrush ecosystem: a symposium: Proceedings; 1978 April; Logan, UT. Logan, UT: Utah State University, College of Natural Resources. 101-109. [518] 7. Bunting, Stephen C.; Kilgore, Bruce M.; Bushey, Charles L. 1987. Guidelines for prescribed burning sagebrush-grass rangelands in the northern Great Basin. Gen. Tech. Rep. INT-231. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 33 p. [5281] 8. Dayton, William A. 1931. Important western browse plants. Misc. Publ. 101. Washington, DC: U.S. Department of Agriculture. 214 p. [768] 9. Dealy, J. Edward. 1971. Habitat characteristics of the Silver Lake mule deer range. Res. Pap. PNW-125. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 99 p. [782] 10. 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] 11. Eckert, Richard E., Jr.; Evans, Raymond A. 1968. Chemical control of low sagebrush and associated green rabbitbrush. Journal of Range Management. 21: 325-328. [841] 12. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 13. 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] 14. Hironaka, M.; Fosberg, M. A.; Winward, A. H. 1983. Sagebrush-grass habitat types of southern Idaho. Bulletin Number 35. Moscow, ID: University of Idaho, Forest, Wildlife and Range Experiment Station. 44 p. [1152] 15. 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] 16. Klebenow, Donald A. 1973. The habitat requirements of sage grouse and the role of fire in management. In: Proceedings, annual Tall Timbers fire ecology conference; 1972 June 8-9; Lubbock, TX. No. 12. Tallahassee, FL: Tall Timbers Research Station: 305-315. [1345] 17. 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] 18. 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] 19. McArthur, E. Durant; Stevens, Richard. 1986. Composite shrubs. Unpublished manuscript on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Labortory, Missoula, MT. 155 p. [7342] 20. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 342 p. [1702] 21. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 22. Schlatterer, Edward F. 1972. A preliminary description of plant communities found on the Sawtooth, White Cloud, Boulder and Pioneer Mountains. Unpublished report. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Region. 111 p. [2076] 23. Schlatterer, E. F. 1973. Sagebrush species and subspecies. Range Improvement Notes. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Region.; 18(2): 1-11. [2077] 24. Sheehy, Dennis P.; Winward, A. H. 1981. Relative palatability of seven Artemisia taxa to mule deer and sheep. Journal of Range Management. 34(5): 397-399. [2128] 25. 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] 26. 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] 27. 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] 28. Tisdale, E. W.; Hironaka, M. 1981. The sagebrush-grass region: a review of the ecological literature. Bull. 33. Moscow, ID: University of Idaho, Forest, Wildlife and Range Experiment Station. 31 p. [2344] 29. 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] 30. Winward, Alma H. 1980. Taxonomy and ecology of sagebrush in Oregon. Station Bulletin 642. Corvallis, OR: Oregon State University, Agricultural Experiment Station. 15 p. [2585] 31. Winward, A. H.; McArthur, E. D.; Kaffer, D. A.; Plummer, C. A.; Brackley, G. K. 1986. Another sagebrush in Nevada. Technical Notes TN-RANGE NV-44. U.S. Department of Agriculture, Nevada Soil Conservation Service. 2 p. [5226] 32. Wright, Henry A.; Neuenschwander, Leon F.; Britton, Carlton M. 1979. The role and use of fire in sagebrush-grass and pinyon-juniper plant communities: A state-of-the-art review. Gen. Tech. Rep. INT-58. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Statio. 48 p. [2625] 33. Young, James A.; Evans, Raymond A. 1971. Medusahead invasion as influenced by herbicides and grazing on low sagebrush sites. Journal of Range Management. 24(6): 451-454. [2648] 34. Young, Richard P. 1983. Fire as a vegetation management tool in rangelands of the Intermountain Region. 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: 18-31. [2681] 35. 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] 36. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of California. Berkeley, CA: University of California Press. 1400 p. [21992]

Index

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