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Introductory

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
ABBREVIATION : BALSAG SYNONYMS : NO-ENTRY SCS PLANT CODE : BASA3 COMMON NAMES : arrowleaf balsamroot breadroot gray dock TAXONOMY : The fully documented scientific name of arrowleaf balsamroot is Balsamorhiza sagittata (Pursh) Nutt. Arrowleaf balsamroot hybridizes with Carey's balsamroot (B. careyana), Hooker balsamroot (B. hookeri), hoary balsamroot (B. incana), rosy balsamroot (B. rosea), and toothed balsamroot (B. serrata) [4]. LIFE FORM : Forb FEDERAL LEGAL STATUS : NO-ENTRY OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : W. C. Fischer 1986 LAST REVISED BY AND DATE : J. L. Holifield, July 1987 AUTHORSHIP AND CITATION : Fischer, William C.; Holifield, J. L. 1987. Balsamorhiza sagittata. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
GENERAL DISTRIBUTION : Arrowleaf balsamroot occurs from the Sierra Nevada of California northward along the east side of the Cascades into British Columbia and east to Saskatchewan, the Black Hills of South Dakota, and Colorado. ECOSYSTEMS : FRES17 Elm - ash - cottonwood FRES20 Douglas-fir FRES21 Ponderosa pine FRES23 Fir - spruce FRES26 Lodgepole pine FRES28 Western hardwoods FRES29 Sagebrush FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES38 Plains grasslands STATES : CA CO MT NV OR SD UT WA BC SK ADMINISTRATIVE UNITS : BIHO BICA BLCA BRCA COLM CODA CRMO DETO DINO FOBU GLAC GRTE LAVO LABE MEVE NOCA ROMO SEQU YELL YOSE ZION BLM PHYSIOGRAPHIC REGIONS : 2 Cascade Mountains 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K012 Douglas-fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K020 Spruce - fir - Douglas-fir forest K021 Southwestern spruce - fir forest K023 Juniper - pinyon woodland K024 Juniper steppe woodland K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K051 Wheatgrass - bluegrass K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K066 Wheatgrass - needlegrass K098 Northern floodplain forest SAF COVER TYPES : 210 Interior Douglas-fir 211 White fir 217 Aspen 219 Limber pine 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Arrowleaf balsamroot occurs in many dry grassland, shrub, and forest habitat types within its range, especially in sagebrush-grass, bitterbrush, mountain-mahogany, open juniper, ponderosa pine, limber pine, and Douglas-fir habitat types. It also occurs in some subalpine fir and aspen habitat types. It is typically abundant in mountain big sagebrush habitats. Published listing arrowleaf balsamroot as an indicator or dominant in community types (cts) or habitat types (hts) are presented below. Area Classification Authority CO: White River- grassland, shrubland & Hess & Wasser 1982 Arapaho NF forest hts wc ID grassland & shrubland hts, cts Tisdale 1986

VALUE AND USE

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Arrowleaf balsamroot provides some degree of forage for cattle, sheep, horses, pronghorn, bighorn sheep, and mule deer. On spring ranges it is an important and palatable forage because it greens up early [28]. Flowering heads are often preferred over the foliage [10]. Arrowleaf balsamroot is utilized year-round but is more palatable during spring and early summer when the foliage is succulent [31]. PALATABILITY : Arrowleaf balsamroot has fair palatability for all classes of livestock and when green is especially palatable to domestic sheep [10,13,27,33]. Mule deer use arrowleaf balsamroot year-round [16]. It is a valuable winter and spring forage for Rocky Mountain elk [15]. Deer mice prefer the seeds [7]. The relish and degree of use shown by livestock and wildlife species for arrowleaf balsamroot in several western states is rated as follows [5,15,16,19]: CO MT UT WY Cattle Fair Fair Fair Fair Sheep Good Good Good Good Horses Fair Good Poor Good Pronghorn ---- ---- Fair Poor Elk ---- Excel. Good Good Mule deer ---- Excel. Good Good White-tailed deer ---- ---- ---- Good Small mammals ---- Fair Good Fair Small nongame birds ---- Good Good Poor Upland game birds ---- Good Good Poor Waterfowl ---- ---- Poor Poor NUTRITIONAL VALUE : Arrowleaf balsamroot has been rated fair in energy value and poor in protein value [5]. On a summer range in the River of No Return Wilderness Area of Idaho, arrowleaf balsamroot was found to have sufficient protein to meet requirements for domestic sheep during June and July but was declining in August. It exceeded required calcium levels but did not meet the phosporus levels set by the National Research Council [6]. COVER VALUE : The degree to which arrowleaf balsamroot provides environmental protection during one or more seasons for wildlife species has been rated as follows [5]: MT UT WY Pronghorn ---- Poor Poor Elk Poor Poor Poor Mule deer Poor Poor Poor White-tailed deer ---- ---- Poor Small mammals Fair Good Poor Small nongame birds Good Good Poor Upland game birds Good Fair Poor Waterfowl ---- Poor Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Arrowleaf balsamroot is rated as having high potential for revegetation of oil shale or coal mined land, and stabilization of roadsides and other critical areas [33]. In the Intermountain region it has only low value for soil stabilization [24]. Arrowleaf balsamroot seed is commonly harvested by hand, but a combine is often used if the terrain permits [22]. Seeds are usually cleaned and sold at 95 percent purity with 40 percent germination [28]. Seeds average 55,000 per pound (121,000/kg) at 100 percent purity [28]. Seeds may be stored for 4 years with good viability [24]. Seed of arrowleaf balsamroot can be broadcast or drilled [24]. However, because arrowleaf balsamroot is very slow growing, Wasser [33] recommended drilling to separate it from more competitive species. The seedbed should be firm, and the seeds should be covered after planting [28]. Fall or winter seeding is recommended [24]. Seedlings of arrowleaf balsamroot are persistant on adapted sites [24]. Seeds from a similar source should be used due to regional variation in cold tolerance [33]. Following seeding, sites should not be grazed for at least two growing seasons [28]. Establishment may take 5 to 10 years [24]. On the best sites, plants may require 3 to 4 years to flower, and 7 to 8 years on more arid sites [28]. When established, arrowleaf balsamroot is competitive and compatible with other species [33]. OTHER USES AND VALUES : In the past, young stalks, roots, and seeds were used as food by Native Americans [20]. MANAGEMENT CONSIDERATIONS : Recently established stands of arrowleaf balsamroot or stands used for seed collection should be protected from grazing [28]. Grazing reduces the seed production for natural spread and also retards seedling development [24]. Established balsamroot is strongly tolerant of grazing [33]. Plummer and others [22] recommended grazing only 50 percent of its foliage.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
GENERAL BOTANICAL CHARACTERISTICS : Arrowleaf balsamroot is a native, cool-season, long-lived perennial forb [29]. The coarse, basal leaves are arrow shaped, with entire margins [24,29]. The flower heads are usually solitary on scapose stems which reach 9 to 24 inches (20-60 cm) in height [29]. Arrowleaf balsamroot grows from a large woody root surmounted by a multicipital caudex [12]. The resinous taproot may grow to several inches in diameter and up to 9 feet (270 cm) in length [26,31]. Fruit of arrowleaf balsamroot is a glabrous achene [29]. RAUNKIAER LIFE FORM : Hemicryptophyte REGENERATION PROCESSES : Sexual reproduction: Arrowleaf balsamroot spreads entirely by seed [24]. Seed is mostly animal disseminated [Shaw, pers. comm. 1987]. Seed yield is generally abundant, but crops are often lost to late frosts, insects, and grazing animals. Viability of seed is often low due to insect damage [24]. A 3-month stratification of 32 degrees Fahrenheit (0 deg C) is required to break dormancy. On sagebrush rangelands, continuous snow cover for 3 months provides for successful cool-moist stratification of seeds [36]. Vegetative reproduction: Arrowleaf balsamroot regenerates vegetatively from the very large (several inches in diameter), deep-seated (up to 9 feet deep), woody taproot surmounted by a many-headed caudex bearing several or many rosettes of leaves and from which new aerial stems arise each year [12,20,26]. However, Mueggler [pers. comm. 1987] points out that it is questionable whether new taproots are formed, which would enable these individual rosettes to become truly individual plants. SITE CHARACTERISTICS : Arrowleaf balsamroot is often a dominant forb on many dry foothills and semiarid mountain rangelands. It prefers well drained, fairly deep soils and open, fairly dry situations, such as southerly exposures, open ridges, and parks, throughout the sagebrush, oakbrush, and ponderosa pine types [22,31]. It also occurs on open sunny slopes in Douglas-fir and aspen forests [31]. Arrowleaf balsamroot is resistant to drought and will tolerate semishade [33]. Sites are often rocky [10]. Arrowleaf balsamroot will occur in moderately alkaline to weakly acidic or saline soils [33]. It is intolerant of shallow water tables but will briefly survive periods of soil saturation [28]. Arrowleaf balsamroot naturally grows between 1,000 and 9,000 feet (305-2,744 m) in elevation [33]. Elevational ranges in several western states are as follows [5]: from 5,500 to 9,800 feet (1,677-2,988 m) in CO 4,500 to 7,600 feet (1,372-2,317 m) in UT 4,400 to 8,500 feet (1,341-2,591 m) in WY 3,200 to 7,000 feet ( 946-2,134 m) in MT Arrowleaf balsamroot commonly grows in mixed stands with Idaho fescue (Festuca idahoensis), bluebunch wheatgrass, big sagebrush (Artemisia tridentata), western juniper (Juniperus occidentalis), Utah juniper (J. osteosperma), and ponderosa pine (Pinus ponderosa) [33]. SUCCESSIONAL STATUS : Facultative Seral Species Arrowleaf balsamroot is a climax indicator in several sagebrush and grassland habitat types. It commonly grows in mixed stands with grasses, other forbs, and shrubs [36]. Arrowleaf balsamroot also does well after disturbances such as fire [36]. SEASONAL DEVELOPMENT : Arrowleaf balsamroot begins growth and flowers early, usually in May, but this may vary as follows [10]: Earliest Most frequent Latest State month month month CO May May June ID April May June MT May May June UT April May June WY May June August A representative phenology from the Upper Snake River plains in southeastern Idaho is as follows [2]: Phenological Avg. date Range state Snow melt Mar 30 -- Growth starts Apr 19 -- Flower stalks appear Apr 26 24 First bloom May 9 35 Full bloom May 25 35 Bloom over Jun 4 -- Seed ripe Jun 14 17 Dissemination begins Jun 18 -- Dissemination over July 9 -- Plant drying Jun 22 32 Plant dried Jul 31 --

FIRE ECOLOGY

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
FIRE ECOLOGY OR ADAPTATIONS : Arrowleaf balsamroot is usually undamaged by fire [34]. Regeneration is from regrowth of the thick caudex [20]. POSTFIRE REGENERATION STRATEGY : Caudex, growing points in soil

FIRE EFFECTS

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
IMMEDIATE FIRE EFFECT ON PLANT : Arrowleaf balsamroot is reported to be undamaged [21] or slightly damaged [25] by fire. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : Arrowleaf balsamroot in Nevada was killed by an August fire, probably as a result of unusually intense soil heating caused by the burnout of adjacent woody sagebrush fuels [37]. PLANT RESPONSE TO FIRE : Arrowleaf balsamroot increases in frequency and density after fire [18]. Existing plants recover rapidly following fire, but an increase in the number of plants must await seed prodction [34]. Increase in plant numbers is especially evident after fire in degraded plant communities [36]. Arrowleaf balsamroot is reported to reestablish to preburn levels within 2 to 5 years in northern Idaho [20]. Arrowleaf balsamroot on a burned area in north-central Idaho averaged 22 percent taller than unburned plants [18]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Arrowleaf balsamroot often becomes a visual dominant after a fire and produces more biomass than unburned plants [3]. Increased densities have been observed by the second growing season after a fire [35]. Plants reproduce slowly until the community becomes closed. Productivity and basal cover of arrowleaf balsamroot are then reduced as perennial grassses and shrubs dominate. Balsamroot may remain in the community a long time in a suppressed state until another fire occurs [3]. FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Balsamorhiza sagittata | Arrowleaf Balsamroot
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. 1958. Seasonal development and yield of native plants on the upper Snake River Plains and their relation to certain climatic factors. Tech. Bull. 1190. Washington, DC: U.S. Department of Agriculture. 68 p. [463] 3. Bunting, Stephen C. 1985. Fire in sagebrush-grass ecosystems: successional changes. In: Sanders, Ken; Durham, Jack, eds. Rangeland fire effects: Proceedings of a symposium; 1984 November 27-29; Boise, ID. Boise, ID: U.S. Department of the Interior, Bureau of Land Management, Idaho State Office: 7-11. [558] 4. Cronquist, Arthur. 1955. Vascular plants of the Pacific Northwest: Part 5: Compositae. Seattle: University of Washington Press. 343 p. [716] 5. Elliott, Charles R.; Flinders, Jerran T. 1984. Plant nutrient levels on two summer ranges in the River of No Return Wilderness Area, Idaho. Great Basin Naturalist. 44(1): 621-626. [859] 7. Everett, Richard L.; Meeuwig, Richard O.; Stevens, Richard. 1978. Deer mouse preference for seed of commonly planted species, indigenous weed seed, and sacrifice foods. Journal of Range Management. 31(1): 70-73. [896] 8. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 9. 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] 10. Hermann, F. J. 1966. Notes on western range forbs: Cruciferae through Compositae. Agric. Handb. 293. Washington, DC: U.S. Department of Agriculture, Forest Service. 365 p. [2852] 11. Hess, Karl; Wasser, Clinton H. 1982. Grassland, shrubland, and forestland habitat types of the White River-Arapaho National Forest. Final Report. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 335 p. [1142] 12. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 13. Holechek, Jerry L.; Vavra, Martin; Skovlin, Jon; Krueger, William C. 1982. Cattle diets in the Blue Mountains of Oregon: I. Grasslands. Journal of Range Management. 35(1): 109-112. [242] 14. 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] 15. Kufeld, Roland C. 1973. Foods eaten by the Rocky Mountain elk. Journal of Range Management. 26(2): 106-113. [1385] 16. Kufeld, Roland C.; Wallmo, O. C.; Feddema, Charles. 1973. Foods of the Rocky Mountain mule deer. Res. Pap. RM-111. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 31 p. [1387] 17. 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] 18. Merrill, Evelyn H.; Mayland, Henry F.; Peek, James M. 1980. Effects of a fall wildfire on herbacious vegetation on xeric sites in the Selway-Bitterroot Wilderness, Idaho. Journal of Range Management. 33(5): 363-367. [1642] 19. Mueggler, W. F.; Stewart, W. L. 1980. Grassland and shrubland habitat types of western Montana. Gen. Tech. Rep. INT-66. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 154 p. [1717] 20. Patterson, Patricia A.; Neiman, Kenneth E.; Tonn, Jonalea. 1985. Field guide to forest plants of northern Idaho. Gen. Tech. Rep. INT-180. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 246 p. [1839] 21. Pechanec, Joseph F.; Stewart, George; Plummer, A. Perry; [and others]. 1954. Controlling sagebrush on rangelands. Farmers' Bulletin 2072. Washington, DC: U.S. Department of Agriculture. 44 p. [1860] 22. 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] 23. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 24. Shaw, Nancy L.; Monsen, Stephen B. 1983. Nonleguminous forbs for rangeland sites. In: Monsen, Stephen B.; Shaw, Nancy, compilers. Managing Intermountain rangelands--improvement of range and wildlife habitats: Proceedings of 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: 123-131. [2121] 25. Smith, Michael A.; Busby, Fee. 1981. Prescribed burning: effective control of sagebrush in Wyoming. RJ-165. Laramie, WY: University of Wyoming, Agriculture Experiment Station. 12 p. [2175] 26. Spence, Liter E. 1937. Root studies of important range plants of the Boise River watershed. Journal of Forestry. 35: 747-754. [77] 27. 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] 28. Stevens, Richard; Shaw, Nancy; Howard, Charles G. 1985. Important nonleguminous forbs for Intermountain ranges. In: Range plant improvement in western North America: Proceedings, annual meeting of the Society for Range Management; 1985 February 14; Salt Lake City, UT. Denver, CO: Society for Range Management: 102-112. [2248] 29. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 30. Tisdale, E. W. 1986. Native vegetation of Idaho. Rangelands. 8(5): 202-207. [2339] 31. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 32. 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] 33. Wasser, Clinton H. 1982. Ecology and culture of selected species useful in revegetating disturbed lands in the West. FWS/OBS-82/56. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service, Office of Biological Services, Western Energy and Land Use Team. 347 p. Available from NTIS, Springfield, VA 22161; PB-83-167023. [2458] 34. 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] 35. Young, James A.; Evans, Raymond A. 1978. Population dynamics after wildfires in sagebrush grasslands. Journal of Range Management. 31(4): 283-289. [2657] 36. Young, James A.; Evans, Raymond A. 1979. Arrowleaf balsamroot and mules ear seed germination. Journal of Range Management. 32(1): 71-74. [2658] 37. Zschaechner, Greg A. 1985. Studying rangeland fire effects: a case study in Nevada. In: Sanders, Ken; Durham, Jack, eds. Rangeland fire effects: Proceedings of the symposium; 1984 November 27-29; Boise, ID. Boise, ID: U.S. Department of the Interior, Bureau of Land Managment, Idaho State Office: 66-84. [2692]

Index

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