Fire Effects Information System (FEIS)
FEIS Home Page

SPECIES: Tetradymia spinosa

INTRODUCTORY


  Photo ©Christopher Christie. Photo courtesy of Las Pilitas Nursery.

AUTHORSHIP AND CITATION:
Howard, Janet L. 2002. Tetradymia spinosa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.usda.gov/database/feis/plants/shrub/tetspi/all.html [].

FEIS ABBREVIATION:
TETSPI

SYNONYMS:
No entry

NRCS PLANT CODE [55]:
TESP2

COMMON NAMES:
shortspine horsebrush
catclaw-horsebrush
cottonthorn
spiny horsebrush
thorny horsebrush

TAXONOMY:
The scientific name of shortspine horsebrush is Tetradymia spinosa Hook. & Arn. (Asteraceae) [16,27,30,53,59,60]. Cronquist and others [16] recognize 2 varieties characterized by relatively short, recurved spines and relatively long, straight spines, respectively:

Tetradymia spinosa var. spinosa
Tetradymia spinosa var. longispina M. E. Jones

LIFE FORM:
Shrub

FEDERAL LEGAL STATUS:
No special status

OTHER STATUS:
No entry


DISTRIBUTION AND OCCURRENCE

SPECIES: Tetradymia spinosa
GENERAL DISTRIBUTION:
Shortspine horsebrush occurs from southeastern Oregon east to Wyoming and south to northwestern New Mexico, Utah, and southern California [16,60], where it is rare [30]. Tetradymia spinosa var. longispina occurs in southern Utah and Nevada, and in Mono County, California [16]. Plants database provides a distributional map of shortspine horsebrush.

ECOSYSTEMS [21]:
FRES29 Sagebrush
FRES30 Desert shrub
FRES35 Pinyon-juniper

STATES:
CA CO ID MT NM NV OR UT WY

BLM PHYSIOGRAPHIC REGIONS [4]:
5 Columbia Plateau
6 Upper Basin and Range
7 Lower Basin and Range
10 Wyoming Basin
12 Colorado Plateau

KUCHLER [31] PLANT ASSOCIATIONS:
K023 Juniper-pinyon woodland
K024 Juniper steppe woodland
K038 Great Basin sagebrush
K040 Saltbush-greasewood
K041 Creosote bush
K042 Creosote bush-bur sage
K055 Sagebrush steppe

SAF COVER TYPES [18]:
238 Western juniper
239 Pinyon-juniper

SRM (RANGELAND) COVER TYPES [50]:
211 Creosote bush scrub
401 Basin big sagebrush
402 Mountain big sagebrush
403 Wyoming big sagebrush
404 Threetip sagebrush
405 Black sagebrush 
406 Low sagebrush
414 Salt desert shrub
501 Saltbush-greasewood
506 Creosotebush-bursage

HABITAT TYPES AND PLANT COMMUNITIES:
Shortspine horsebrush is common throughout the Great Basin and Mojave deserts, but does not occur in pure stands. It is usually found as isolated individuals or small colonies in saltbush (Atriplex spp.) scrub, desert steppe, low-elevation sagebrush (Artemisia spp.), and pinyon-juniper (Pinus-Juniperus spp.) communities [3,30,37]. Common Great Basin associates of shortspine horsebrush include shadscale (Atriplex confertifolia), winterfat (Krascheninnikovia lanata), and broom snakeweed (Gutierrezia sarothrae) [3]. In Utah it occurs in desert shrub, shrub-grassland, and Colorado pinyon-Utah juniper communities (P. edulis-J. osteosperma) [60]. It is a subdominant shrub on the Snake River Plain of southern Idaho, where it associates with big sagebrush (Artemisia tridentata), winterfat, and snakeweeds (Gutierrezia spp.) [33,40]. It is most common in black greasewood (Sarcobatus vermiculatus)-shadscale communities in Nevada [6,8], and in saltbush scrub deserts in California [27]. It also occurs in big sagebrush, creosotebush (Larrea tridentata), singleleaf pinyon (P. monophylla), and Joshua tree (Yucca brevifolia) communities in California [2,24].

Although shortspine horsebrush is fairly constant in desert plant communities, it is usually not a community dominant. It showed 33% constancy in a shortspine hopsage/green rabbitbrush/cheatgrass (Grayia spinosa/Chrysothamnus viscidiflorus/Bromus tectorum) community in north-central Nevada [5], and 38% mean cover on Mojave Desert sites in California [14]. It sometimes forms a Nevada ephedra (Ephedra nevadensis)-shortspine horsebrush association in the Mojave Desert [13]. Branson and others [7] documented a shortspine horsebrush-dominated community in west-central Colorado. It was the least productive and least diverse of the 13 Colorado Great Basin communities they studied.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Tetradymia spinosa
GENERAL BOTANICAL CHARACTERISTICS:
Shortspine horsebrush is a native subshrub or shrub with semiwoody to woody stem texture [30], reaching 4 feet (1.2 m) in height [16]. The leaves and young shoots are armed with spines [27,30,59] that are 0.2 to 0.6 inch (0.5-1.5 cm) long in the typical variety and 0.6 to 2 inches (1.5-5.0 cm) in Tetradymia spinosa var. longispina [16]. Horsebrushes (Tetradymia spp.) have 2 types of leaves: primary and secondary. Primary leaves occur on elongated stems, and secondary leaves grow from the axils of primary leaves [35]. Shortspine horsebrush's inflorescence is a raceme with tubular, perfect flowers [16,35]. Fruits are 6- to 8-mm-long hairy achenes with bristly pappi [27]. Shortspine horsebrush is rhizomatous, and shows a strong tendency to form colonies [53]. Horsebrushes are tap-rooted [32]. 

RAUNKIAER [47] LIFE FORM:
Phanerophyte

REGENERATION PROCESSES:
Shortspine horsebrush regenerates from seed and by sprouting from rhizomes and the root crown [9,41,56,61,62]. Information on seed production, viability, and dispersal, seed banking, and seedling establishment is scant for shortspine and other horsebrushes. Further research is needed on the reproductive ecology of this genus.

Breeding system: Shortspine horsebrush may often be self-fertilized by individuals within a colony connected by rhizomes [53].

Pollination: Horsebrushes are pollinated by insect generalists including flies, moths, bees, and beetles [35].

Seed dispersal: Horsebrush seeds are wind dispersed [64]. The hairs on horsebrush pappi aid dispersal [20].

Seedling establishment/growth: Seedling establishment is rare in horsebrushes, probably due to harsh environments [53]. Shortspine horsebrush seedlings were observed on a prescribed burned site in southeastern Oregon [62].

Asexual regeneration: Shortspine horsebrush forms small colonies from rhizomes, which may extend 1 foot (30 cm) from the parent plant [37,53]. It also sprouts from the root crown [41,61].

SITE CHARACTERISTICS:
Shortspine horsebrush occurs on dry, open foothills, plains, and alkali sinks [16,34]. It grows on skeletal to deep soils [5,24] with clay and loam textures [5,59]. Sites with a large shortspine horsebrush component are often mostly bare ground. In west-central Colorado, a shortspine horsebrush community showed 15% plant cover (9% of which was shortspine horsebrush), 8% litter cover, and 77% bare soil. Although the soil was moist, it was the saltiest of 13 plant communities studied. Researchers speculated that most soil water was lost to evaporation [7]. A northeastern Utah study found shortspine horsebrush dominance was correlated with bare ground and soils with poor cation exchange and high concentrations of soluble salts [10].

Shortspine horsebrush generally occurs from 2,600 to 6,600 feet (800-2,000 m) elevation, although it is rarely found as high as 8,900 feet (2,700 m) [16]. Elevational ranges by state are:

CA 2,600-7,900 feet (800-2,400 m) [24,27]
CO 4,500-7,000 feet (1,400-2,100) [26]
UT 1,400-6,300 feet (1,250-1,925 m) [60]

Climate on shortspine horsebrush sites is often harsh, with hot summers and cool to cold winters. A Nevada ephedra-shortspine horsebrush site in the Owens Valley of California showed a mean weekly maximum summer temperature of 104 oFahrenheit (40 oC), 0.9 inch (240 mm) total summer precipitation, and mean total windspeed of 62.1 miles/day (99.9 km/day) [13].

SUCCESSIONAL STATUS:
Shortspine horsebrush occurs in both seral and late-successional plant communities [44]. The rate of succession in many salt desert shrublands is very slow [58], and as a sprouting species, shortspine horsebrush is more likely to be found in seral communities compared to nonsprouting desert shrubs. Shortspine horsebrush is a nurse plant for seedling cholla cacti (Opuntia spp.) in the Mojave Desert [15].

SEASONAL DEVELOPMENT:
Shortspine horsebrush flowers from April to June [16]; occasionally flowering extends into August [34]. Colonies usually have synchronous flowering [37,53]. Failure to flower or develop seed is apparently triggered by low rainfall. In very dry years, some individuals -- or entire colonies -- may not flower, or will flower and not set seed [53]. Shortspine horsebrush is drought deciduous, shedding the secondary leaves 1st [23,53].

FIRE ECOLOGY

SPECIES: Tetradymia spinosa
FIRE ECOLOGY OR ADAPTATIONS:
Fire adaptations: Horsebrushes are "slightly damaged by fire" [45]: top-growth is removed. Shortspine horsebrush sprouts from the root crown and rhizomes after fire [9,41,56,61]. It also establishes from seed after fire [62].

Fire regimes: Fires in the desert shrub ecosystems in which shortspine horsebrush occurs were historically infrequent and stand replacing. Shortspine horsebrush is most common on dry sites with sparse vegetation cover [7,10], and fires are rare on shortspine horsebrush-dominated sites due to sparse fuels [41,42]. Fires in the pinyon-juniper types with a shortspine horsebrush component were of mixed severity [42].

The following table provides fire return interval for plant communities and ecosystems with shortspine horsebrush. Find further fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes".

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 [42]
basin big sagebrush Artemisia tridentata var. tridentata 12-43 [48]
mountain big sagebrush Artemisia tridentata var. vaseyana 15-40 [1,11,36]
Wyoming big sagebrush Artemisia tridentata var. wyomingensis 10-70 (40**) [57,63]
saltbush-greasewood Atriplex confertifolia-Sarcobatus vermiculatus < 35 to < 100
western juniper Juniperus occidentalis 20-70
Rocky Mountain juniper Juniperus scopulorum < 35 
pinyon-juniper Pinus-Juniperus spp. < 35 [42]
**mean

POSTFIRE REGENERATION STRATEGY [51]:
Small shrub, adventitious bud/root crown
Rhizomatous shrub, rhizome in soil

FIRE EFFECTS

SPECIES: Tetradymia spinosa
IMMEDIATE FIRE EFFECT ON PLANT:
Fire rarely kills horsebrush species. It top-kills shortspine horsebrush [43,45].

DISCUSSION AND QUALIFICATION OF FIRE EFFECT:
No entry

PLANT RESPONSE TO FIRE:
Shortspine horsebrush establishes after fire from seed and by sprouting from rhizomes and the root crown [9,41,56,61]. Shortspine horsebrush seedlings were observed 1 year after prescribed burning in a Wyoming big sagebrush (Artemisia tridentata ssp. wyomingensis) community in southeastern Oregon [62]. Whether the seedlings established from the seed bank or from off-site sources was not known.

DISCUSSION AND QUALIFICATION OF PLANT RESPONSE:
No entry

FIRE MANAGEMENT CONSIDERATIONS:
Fire exclusion on desert steppes has tended to favor sagebrush species over fire-tolerant shrubs such as shortspine horsebrush [12,25,28]. Increased fire frequencies due to invasion of cheatgrass, red brome (Bromus madritensis ssp. rubens), and other annual grasses may favor shortspine horsebrush and other sprouting shrubs over sagebrush.

MANAGEMENT CONSIDERATIONS

SPECIES: Tetradymia spinosa
IMPORTANCE TO LIVESTOCK AND WILDLIFE:
Palatability: Shortspine horsebrush is not a toxic horsebrush species [19,49,52,54], but browsers seldom use it. Horsebrushes are unpalatable except early in the spring, when animals may consume young shoots and buds [29,49]. Domestic sheep on saltdesert shrublands in Utah browsed shortspine horsebrush only incidentally. Use was 0.9% in the 1st year of the study and 0% in the 2nd [22]. Palatability of shortspine horsebrush has been rated as follows [17]:

  CO MT UT WY
cattle ---- poor poor poor
domestic sheep ---- poor fair poor
horses ---- poor poor poor
pronghorn ---- ---- poor ----
elk poor ---- poor ----
mule deer poor ---- poor ----
small mammals ---- ---- fair ----
small nongame birds ---- ---- fair ----
upland game birds ---- ---- poor ----
waterfowl ---- ---- poor ----

Nutritional value: Mean nutritional content of shortspine horsebrush browse is as follows [39]:

Nutrient %
ash 5.4
crude fiber 36.8
ether extract 6.3
N-free extract 42.8
Protein (N × 6.25) 8.7
     cattle (digestible protein) 5.3
     domestic goats (digestible protein) 4.7
     horses (digestible protein) 4.9
     domestic rabbits (digestible protein) 5.4
     domestic sheep (digestible protein) 5.1
calcium 0.94
phosphorus 0.25

Cover value: Shortspine horsebrush provides cover for small animals [34].

VALUE FOR REHABILITATION OF DISTURBED SITES:
Shortspine horsebrush helps stabilize soil on erodible desert sites. Horsebrushes provide critically needed ground cover on dry sites that are otherwise often sparsely vegetated [34].

OTHER USES:
Shortspine horsebrush is a honeybee plant [30]. Western Shoshone used shortspine horsebrush concoctions as external medicine, and used the spines as piercing instruments [65].

OTHER MANAGEMENT CONSIDERATIONS:
Shortspine horsebrush was affected by the massive shrub die-off in the Great Basin in 1977-1986. Besides high mortality, many plants showed signs of decline and low vigor. Causes of the die-off are not known; unlike other periods of shrub die-off in the Great Basin, it occurred during a period of unusually high precipitation [33,40]. Elevated levels of soil salinity, anaerobic conditions caused by waterlogged soils, and plant pathogens (viruses, fungi, and bacteria) have been suggested as causes. One result of the die-back was an escalated invasion of cheatgrass, which established in areas left bare by dead shrubs [40]. See cheatgrass for information on altered fire regimes due to that species.

Tetradymia spinosa: References


1. Arno, Stephen F.; Gruell, George E. 1983. Fire history at the forest-grassland ecotone in southwestern Montana. Journal of Range Management. 36(3): 332-336. [342]

2. Bauer, H. L. 1930. Vegetation of the Tehachapi Mountains, California. Ecology. 11(2): 263-280. [15102]

3. Beale, Donald M.; Smith, Arthur D. 1970. Forage use, water consumption, and productivity of pronghorn antelope in western Utah. Journal of Wildlife Management. 34(3): 570-582. [6911]

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. Blackburn, Wilbert H.; Tueller, Paul T.; Eckert, Richard E., Jr. 1968. Vegetation and soils of the Mill Creek Watershed. Reno, NV: University of Nevada, College of Agriculture. 71 p. In cooperation with: U.S. Department of the Interior, Bureau of Land Management. [12500]

6. 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]

7. Branson, Farrel A.; Miller, Reuben F.; McQueen, I. S. 1976. Moisture relationships in twelve northern desert shrub communities near Grand Junction, Colorado. Ecology. 57(6): 1104-1124. [510]

8. Breck, Stewart W.; Jenkins, Stephen H. 1997. Use of an ecotone to test the effects of soil and desert rodents on the distribution of Indian ricegrass. Ecography. 20(3): 253-263. [29188]

9. Britton, Carlton M.; Wright, Henry A. 1983. Brush management with fire. In: McDaniel, Kirk C., ed. Proceedings: brush management symposium; 1983 February 16; Albuquerque, NM. Denver, CO: Society for Range Management: 61-68. [521]

10. Brotherson, Jack D.; Brotherson, Karen J. 1979. Ecological and community relationships of Eriogonum corymbosum (Polygonaceae) in the Uinta Basin, Utah. The Great Basin Naturalist. 39(2): 177-191. [530]

11. Burkhardt, Wayne J.; Tisdale, E. W. 1976. Causes of juniper invasion in southwestern Idaho. Ecology. 57: 472-484. [565]

12. Butler, Bret W.; Reynolds, Timothy D. 1997. Wildfire case study: Butte City Fire, southeastern Idaho, July 1, 1994. Gen. Tech. Rep. INT-GRT-351. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 15 p. [27526]

13. Chabot, Brian F.; Billings, W. D. 1972. Origins and ecology of the Sierran alpine flora and vegetation. Ecological Monographs. 42(2): 163-199. [11228]

14. Cody, M. L. 1986. Spacing patterns in Mojave Desert plant communities: near-neighbor analyses. Journal of Arid Environments. 11: 199-217. [4411]

15. Cody, Martin L. 1993. Do cholla cacti (Opuntia spp., subgenus Cylindropuntia) use or need nurse plants in the Mojave Desert? Journal of Arid Environments. 24: 139-154. [22628]

16. Cronquist, Arthur; Holmgren, Arthur H.; Holmgren, Noel H.; [and others]. 1994. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 5. Asterales. New York: The New York Botanical Garden. 496 p. [28653]

17. 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]

18. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905]

19. Fleming, C. E.; Miller, M. R.; Vawter, L. A. 1922. The spring rabbit-brush: a range plant poisonous to sheep. Bulletin No. 104. Reno, NV: The University of Nevada. 29 p. [41407]

20. Fort, Kevin P.; Richards, James H. 1998. Does seed dispersal limit initiation of primary succession in desert playas? American Journal of Botany. 85(12): 1722-1731. [30069]

21. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; Lewis, Mont E.; Smith, Dixie R. 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]

22. Green, Lisle R.; Sharp, Lee A.; Cook, C. Wayne; Harris, Lorin E. 1951. Utilization of winter range forage by sheep. Journal of Range Management. 4: 233-241. [7891]

23. Hacke, Uwe G.; Sperry, John S.; Pitterman, Jarmila. 2000. Drought experience and cavitation resistance in six shrubs from the Great Basin, Utah. Basic Applied Ecology. 1: 31-41. [41409]

24. Hanes, Ted L. 1976. Vegetation types of the San Gabriel Mountains. In: Latting, June, ed. Symposium proceedings: plant communities of southern California; 1974 May 4; Fullerton, CA. Special Publication No. 2. Berkeley, CA: California Native Plant Society: 65-76. [4227]

25. Harniss, Roy O.; Murray, Robert B. 1973. 30 years of vegetal change following burning of sagebrush-grass range. Journal of Range Management. 26(5): 322-325. [1086]

26. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press, Inc. 666 p. [6851]

27. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of California. Berkeley, CA: University of California Press. 1400 p. [21992]

28. Houston, Douglas B. 1973. Wildfires in northern Yellowstone National Park. Ecology. 54(5): 1111-1117. [5781]

29. Johnson, A. Earl. 1987. The relationship of Tetradymia species and Artemisia nova to photosensitization in sheep. In: Provenza, Frederick D.; Flinders, Jerran T.; McArthur, E. Durant, compilers. Proceedings--symposium on plant-herbivore interactions; 1985 August 7-9; Snowbird, UT. Gen. Tech. Rep. INT-222. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 113-117. [1270]

30. Kartesz, John T.; Meacham, Christopher A. 1999. Synthesis of the North American flora (Windows Version 1.0), [CD-ROM]. Available: North Carolina Botanical Garden. In cooperation with the Nature Conservancy, Natural Resources Conservation Service, and U.S. Fish and Wildlife Service [2001, January 16]. [36715]

31. Kuchler, A. W. 1964. United States [Potential natural vegetation of the conterminous United States]. Special Publication No. 36. New York: American Geographical Society. 1:3,168,000; colored. [3455]

32. Manning, Sara J.; Groeneveld, David P. 1990. Shrub rooting characteristics and water acquisition on xeric sites in the western Great Basin. In: McArthur, E. Durant; Romney, Evan M.; Smith, Stanley D.; Tueller, Paul T., compilers. Proceedings--symposium on cheatgrass invasion, shrub die-off, and other aspects of shrub biology and management; 1989 April 5-7; Las Vegas, NV. Gen. Tech. Rep. INT-276. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 238-244. [12856]

33. Maskarinec, Gary S. 1994. Native plant die-offs. In: Despain, Don G., ed. Plants and their environments: Proceedings of the 1st biennial scientific conference on the Greater Yellowstone Ecosystem; 1991 September 16-17; Yellowstone National Park, WY. Tech. Rep. NPS/NRYELL/NRTR. Denver, CO: U.S. Department of the Interior, National Park Service, Rocky Mountain Region, Yellowstone National Park: 199-204. [26285]

34. 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]

35. 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 Laboratory, Missoula, MT. 155 p. [7342]

36. Miller, Richard F.; Rose, Jeffery A. 1995. Historic expansion of Juniperus occidentalis (western juniper) in southeastern Oregon. The Great Basin Naturalist. 55(1): 37-45. [26637]

37. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 342 p. [1702]

38. Mueggler, Walter F. 1950. Effects of spring and fall grazing by sheep on vegetation of the upper Snake River plains. Journal of Range Management. 3: 308-315. [1703]

39. National Academy of Sciences. 1971. Atlas of nutritional data on United States and Canadian feeds. Washington, DC: National Academy of Sciences. 772 p. [1731]

40. Nelson, David L.; Harper, Kimball T.; Boyer, Kenneth C.; [and others]. 1989. Wildland shrub dieoffs in Utah: an approach to understanding the cause. In: Wallace, Arthur; McArthur, E. Durant; Haferkamp, Marshall R., compilers. Proceedings--symposium on shrub ecophysiology and biotechnology; 1987 June 30 - July 2; Logan, UT. Gen. Tech. Rep. INT-256. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 119-135. [5942]

41. Neuenschwander, L. F. 1978. The fire induced autecology of selected shrubs of the cold desert and surrounding forests: A-state-of-the-art review. Unpublished manuscript on file at: U.S. Department of Agriculture, Forest Service, Intermountain Fire Sciences Laboratory, Missoula, MT. 31 p. [1747]

42. Paysen, Timothy E.; Ansley, R. James; Brown, James K.; [and others]. 2000. Fire in western shrubland, woodland, and grassland ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-volume 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 121-159. [36978]

43. Pechanec, Joseph F.; Plummer, A. Perry; Robertson, Joseph H.; Hull, A. C., Jr. 1965. Sagebrush control on rangelands. Agriculture Handbook No. 277. Washington, DC: U.S. Department of Agriculture. 40 p. [1858]

44. Phillips, Edwin A.; Page, Karen K.; Knapp, Sandra D. 1980. Vegetational characteristics of two stands of Joshua tree woodland. Madrono. 27(1): 43-47. [5809]

45. Ralphs, Michael H.; Schen, David C.; Busby, Fee. 1975. Prescribed burning--effective control of sagebrush and open juniper. Utah Science. 36(3): 94-98. [1931]

46. Ralphs, Michael H.; Schen, David C.; Busby, Frank E. 1976. General considerations necessary in planning a prescribed burn. In: Use of prescribed burning in western woodland and range ecosystems: Proceedings of the symposium; 1976 March 18-19; Logan, UT. Logan, UT: Utah State University, Utah Agricultural Experiment Station: 49-53. [1932]

47. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843]

48. Sapsis, David B. 1990. Ecological effects of spring and fall prescribed burning on basin big sagebrush/Idaho fescue--bluebunch wheatgrass communities. Corvallis, OR: Oregon State University. 105 p. Thesis. [16579]

49. Schuster, Joseph L.; James, Lynn F. 1988. Some other major poisonous plants of the western United States. In: James, Lynn F.; Ralphs, Michael; Nielsen, Darwin B., eds. The ecology and economic impact of poisonous plants on livestock production. Westview Special Studies in Agriculture Science and Policy. Boulder, CO: Westview Press: 295-307. [41408]

50. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. [23362]

51. Stickney, Peter F. 1989. FEIS postfire regeneration workshop--April 12: Seral origin of species comprising secondary plant succession in Northern Rocky Mountain forests. 10 p. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. [20090]

52. Stoddart, L. A.; Holmgren, A. H.; Cook, C. W. 1949. Important poisonous plants of Utah. Special Report No. 2. Logan, UT: Utah State Agricultural College, Agricultural Experiment Station. 21 p. [2259]

53. Strother, John L. 1974. Taxonomy of Tetradymia (Compositae: Senecioneae). Brittonia. 26: 177-202. [2268]

54. U.S. Department of Agriculture, Agricultural Research Service. 2002. Horsebrush (Tetradymia glabrata, T. canescens). In: Agriculture Information--Bulletin 415: Plants poisonous to livestock in the western states, [Online]. Available: http://www.pprl.usu.edu/horsebrush.htm [2002, August 6]. [41588]

55. U.S. Department of Agriculture, Natural Resources Conservation Service. 2005. PLANTS database (2005), [Online]. Available: https://plants.usda.gov /. [34262]

56. Urness, Philip J. 1979. Wildlife habitat manipulation in sagebrush ecosystems. In: The sagebrush ecosystem: a symposium: Proceedings; 1978 April; Logan, UT. Logan, UT: Utah State University, College of Natural Resources: 169-178. [2404]

57. Vincent, Dwain W. 1992. The sagebrush/grasslands of the upper Rio Puerco area, New Mexico. Rangelands. 14(5): 268-271. [19698]

58. Webb, Robert H.; Steiger, John W.; Newman, Evelyn B. 1988. The response of vegetation to disturbance in Death Valley National Monument, California. U.S. Geological Survey Bulletin 1793. Washington, DC: U.S. Department of the Interior, Geological Survey. 69 p. [8915]

59. Weber, William A. 1987. Colorado flora: western slope. Boulder, CO: Colorado Associated University Press. 530 p. [7706]

60. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. The Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. [2944]

61. 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 Station. 48 p. [2625]

62. Wrobleski, David W. 1999. Effects of prescribed fire on Wyoming big sagebrush communities: implications for ecological restoration of sage grouse habitat. Corvallis, OR: Oregon State University. 76 p. Thesis. [2644]

63. Young, James A.; Evans, Raymond A. 1981. Demography and fire history of a western juniper stand. Journal of Range Management. 34(6): 501-505. [2659]

64. 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 of symposia; 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]

65. Zigmond, Maurice L. 1981. Kawaisu ethnobotany. Salt Lake City, UT: University of Utah Press. 102 p. [35936]


FEIS Home Page
https://www.fs.usda.gov/database/feis/plants/shrub/tetspi/all.html