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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > Species: Tetradymia nuttallii | Nuttall Horsebrush
 

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Introductory

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
ABBREVIATION : TETNUT SYNONYMS : NO-ENTRY SCS PLANT CODE : TENU2 COMMON NAMES : Nuttall horsebrush TAXONOMY : Strother's 1974 revision of the genus Tetradymia recognizes Nuttall horsebrush as Tetradymia nuttallii Torr. & Gray. Strother put in synonymy with T. glabrata the two entities, T. spinosa Nutt. and X T. permizta Payson [9]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Kathy Ahlenslager, May 1986 LAST REVISED BY AND DATE : Kathleen E. Ahlenslager December 1987 AUTHORSHIP AND CITATION : Ahlenslager, Kathleen E. 1987. Tetradymia nuttallii. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
GENERAL DISTRIBUTION : Nuttall horsebrush grows in the badlands of southwestern Wyoming, as well as in dry barren hills and plains of northeastern Nevada, northern Utah, and northwestern Colorado. ECOSYSTEMS : FRES29 Sagebrush FRES30 Desert shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES40 Desert grasslands STATES : CO NV UT WY ADMINISTRATIVE UNITS : DINO BLM PHYSIOGRAPHIC REGIONS : 3 Southern Pacific Border 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 7 Lower Basin and Range 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K23 Juniper - pinyon woodland K38 Great Basin sagebrush K40 Saltbrush - greasewood K51 Wheatgrass - bluegrass K53 Grama - galleta steppe K55 Sagebrush steppe K63 Foothills prairie SAF COVER TYPES : 239 Pinyon - juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Because Nuttall horsebrush is a seral species, it is not found as a dominant, codominant, or indicator species in any habitat types. It is usually associated with sagebrush and shadscale vegetation types [7].

VALUE AND USE

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Nuttall horsebrush is browsed in winter and early spring on desert ranges and overgrazed areas. It provides needed ground cover on dry desert ranges [7]. PALATABILITY : Nuttall horsebrush is low in palatability. Palatability ratings for different livestock and wildlife species in Utah are as follows [4]: Cattle Poor Sheep Poor Horses Poor Pronghorn Poor Elk Poor Mule deer Poor Small mammals Fair Small nongame birds Poor Upland game birds Poor Waterfowl Poor NUTRITIONAL VALUE : Nuttall horsebrush is rated poor in energy and protein value [4]. COVER VALUE : The degree to which Nuttall horsebrush provides environmental protection during one or more seasons for wildlife species in Utah is as follows [4]: Pronghorn Poor Elk Poor Mule deer Poor Small mammals Fair Small nongame birds Fair Upland game birds Fair Waterfowl Poor VALUE FOR REHABILITATION OF DISTURBED SITES : OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : NO-ENTRY

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
GENERAL BOTANICAL CHARACTERISTICS : Nuttall horsebrush is a native, perennial, rigidly branched shrub that grows up to 4 feet (12 dm) tall [8,10]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Nuttall horsebrush regenerates vegetatively through root crown sprouting, as well as sexually via wind-dispersed seeds. Although flowers are highly fertile, seedlings are rarely observed in nature. This is probably due to the harsh environment in which this species occurs [9]. SITE CHARACTERISTICS : Nuttall horsebrush plants occur in sagebrush and shadscale communities on badlands, and dry barren hills and plains from 4,300 to 6,900 feet (1,300-2,100 m) [9]. Elevational ranges vary as follows [4]: from 5,600 to 6,500 feet (1,707-1,982 m) in CO 4,500 to 6,000 feet (1,372-1,829 m) in UT 6,200 to 6,200 feet (1,890-1,890 m) in WY SUCCESSIONAL STATUS : Nuttall horsebrush is a seral species and has the ability to increase in abundance during secondary succession through vigorously sprouting root crowns. Although flowers are highly fertile, seedlings are rarely observed in nature. This is probably due to the harsh environment in which this species occurs [4]. SEASONAL DEVELOPMENT : Nuttall horsebrush plants generally bloom from late May to early July [10]. Flowering dates are as follows [4]: State Earliest date oberved Latest date observed CO July July UT June June WY June August As typical with many xerophytes, the occurrence of flowering is correlated with distribution and rainfall. In very dry years some individuals or entire colonies do not bloom at all, or bloom but fail to mature fruits, probably due to decreases in water availability [9]. One way xerophytic species cope with a short growing season is by maturing flowers simultaneously. Often whole colonies of plants will bloom at once, and most horsebrush plants within a colony will flower within a few days of each other [9].

FIRE ECOLOGY

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
FIRE ECOLOGY OR ADAPTATIONS : Plants of Nuttall horsebrush stand dormant throughout most of the year on the dry ranges where they occur. During a fire these much-branched shrubs burn rapidly, with little heat transferred downward into the root crowns. Fire stimulates the root crowns to sprout [10]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown Ground residual colonizer (on-site, initial community)

FIRE EFFECTS

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
IMMEDIATE FIRE EFFECT ON PLANT : The effect of fire on shrubs is more damaging than that on forbs and grasses. Fire not only destroys herbage, but destroys the stored reserves of shrubs [3]. Nuttall horsebrush is considered a fire-resistant species, as there is a 65 percent or greater chance that at least 50 percent of a population will survive or reestablish after a fire [10,11]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Nuttall horsebrush, which is capable of resprouting and rapid regrowth after a fire, is favored over other plants that reestablish only by seed [2]. Postfire regeneration response is considered rapid with 2 to 5 years required to approximate preburn frequency or cover [10]. Plants quickly regain and surpass their original size. The amount of sprouting is affected by season and soil moisture, as these are factors which contribute to burning intensity [3]. After a fire, crown-sprouting Nuttall horsebrush may initially dominate sagebrush ranges. In addition to the vigorous postburn production of root crown sprouts, there is dynamic seedling establishment [12]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Tetradymia nuttallii | Nuttall Horsebrush
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. Blaisdell, James P. 1953. Ecological effects of planned burning of sagebrush-grass range on the upper Snake River Plains. Tech. Bull. 1975. Washington, DC: U.S. Department of Agriculture. 39 p. [462] 3. 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] 4. 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] 5. 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] 6. 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] 7. 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] 8. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 9. Strother, John L. 1974. Taxonomy of Tetradymia (Compositae: Senecioneae). Brittonia. 26: 177-202. [2268] 10. Volland, Leonard A.; Dell, John D. 1981. Fire effects on Pacific Northwest forest and range vegetation. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region, Range Management and Aviation and Fire Management. 23 p. [2434] 11. Wright, Henry A. 1972. Shrub response to fire. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., eds. Wildland shrubs--their biology and utilization: Proceedings of a symposium; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 204-217. [2611] 12. 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]

Index

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Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

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