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Introductory

SPECIES: Aster conspicuus | Showy Aster
ABBREVIATION : ASTCON SYNONYMS : NO-ENTRY SCS PLANT CODE : ASCO3 COMMON NAMES : showy aster conspicuous aster creeping aster TAXONOMY : The currently accepted scientific name of showy aster is Aster conspicuus Lindl. [10,14]. There are no recognized subspecies, varieties, or forms. LIFE FORM : Forb FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : William R. Reed, September 1993 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Reed, William R. 1993. Aster conspicuus. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Aster conspicuus | Showy Aster
GENERAL DISTRIBUTION : Showy aster is distributed from Yukon Territory east to Saskatchewan, south to northern Wyoming, and west to northeastern Oregon [10,14]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir - spruce FRES25 Larch FRES26 Lodgepole pine FRES29 Sagebrush STATES : ID MT OR WA WY AB BC SK YT ADMINISTRATIVE UNITS : BIHO GLAC GRTE NOCA YELL BLM PHYSIOGRAPHIC REGIONS : 2 Cascade Mountains 5 Columbia Plateau 8 Northern Rocky Mountains 9 Middle Rocky Mountains 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K002 Cedar - hemlock - Douglas-fir forest K004 Fir - hemlock forest K008 Lodgepole pine - subalpine forest K010 Ponderosa shrub forest K011 Western ponderosa forest K012 Douglas-fir forest K013 Cedar - hemlock - pine forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest K055 Sagebrush steppe SAF COVER TYPES : 201 White spruce 205 Mountain hemlock 206 Engelmann spruce - subalpine fir 207 Red fir 210 Interior Douglas-fir 211 White fir 212 Western larch 213 Grand fir 215 Western white pine 218 Lodgepole pine 219 Limber pine 237 Interior ponderosa pine 251 White spruce - aspen SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Common plant associates of showy aster include heartleaf arnica (Arnica cordifolia), Lindley aster (Aster ciliolatus), pinegrass (Calamagrostis rubescens), white spiraea (Spiraea betulifolia), huckleberry (Vaccinium spp.), and elk sedge (Carex geyeri).

VALUE AND USE

SPECIES: Aster conspicuus | Showy Aster
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Showy aster is a common constituent of summmer diets of black bear in lodgepole pine (Pinus contorta) forests of Alberta [11]. Showy aster is preferred forage for grizzly bears in the Bob Marshall Wilderness Area, northwestern Montana [17]. PALATABILITY : Showy aster provides valuable forage for deer, elk, cattle, and domestic sheep in Idaho and British Columbia [18,21]. NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Showy aster is low in resistance to repeated human trampling, but it may recover rapidly. In montane grassland in Montana, showy aster cover increased more than 30 percent between the end of August and the following June [3]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Showy aster cover decreased from 4.4 to 0.7 percent under heavy grazing in a Douglas-fir forest in northern Idaho [27]. It also declined in abundance and vigor following heavy grazing in a Douglas-fir vegetation type in British Columbia [25], and decreased to 0.0 percent frequency following 12 years of heavy grazing in a mountain meadow community in northern Idaho [15]. Showy aster increased following clearcutting in a Douglas-fir/ninebark (Physocarpus malvaceus) habitat type in western Montana [1].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Aster conspicuus | Showy Aster
GENERAL BOTANICAL CHARACTERISTICS : Showy aster is a native, perennial herb. Its peduncle is 1 to 2 feet (30-60 cm) tall, and it usually has several shorter sterile stems arising from extensive creeping rhizomes [14]. Rhizomes grow 0.5 to 2.0 inches (0.5-5 cm) below the soil surface [4]. Flowers are borne in an open, flat-topped inflorescence [10,14]. RAUNKIAER LIFE FORM : Geophyte REGENERATION PROCESSES : Sexual: Showy aster reproduces by seed. Seeds are wind dispersed long distances and can germinate on bare soil [5,18,20]. Asexual: Showy aster sprouts from extensive, creeping rhizomes [4,18]. SITE CHARACTERISTICS : Showy aster occurs in continental boreal and cool-temperate climates on moderately dry soils. It is a common interior species on "water shedding" sites [12]. It is most common in montane zones, but is also found in forested areas of valley and lower subalpine zones [14]. In Wyoming showy aster occurs from 5,500 to 9,000 feet (1,667-2,727 m) elevation. In Montana it is found from 3,000 to 7,100 feet (910-2,152 m) elevation [6]. SUCCESSIONAL STATUS : Facultative Seral Species Showy aster is tolerant of both sun and shade. Small colonies typically establish following stand-destroying fires or clearcutting and site scarification [20,22]. Showy aster produces more vegetative growth and fewer flowering stems with increasing shade in later succession [14]. It can, however, maintain extensive colonies beneath pine (Pinus spp.) and open Douglas-fir canopies. It is an indicator of late seres in Douglas fir/ninebark (Physoparpus malvaceus) habitat types of central Idaho [20]. SEASONAL DEVELOPMENT : Showy aster flowers in late summer throughout its range [14].

FIRE ECOLOGY

SPECIES: Aster conspicuus | Showy Aster
FIRE ECOLOGY OR ADAPTATIONS : Showy aster is moderately resistant to fire, typically sprouting from surviving rhizomes. Rhizomes usually survive light- to moderate-severity fires that do not cause excessive soil heating [4,8]. After fire, showy aster also regenerates from wind-dispersed and soil-stored seed [5,20,24]. Growth is stimulated after fire, resulting in mass flowering in the first few postfire years [22,23,24]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Ground residual colonizer (on-site, initial community) Initial-offsite colonizer (off-site, initial community) Secondary colonizer - on-site seed

FIRE EFFECTS

SPECIES: Aster conspicuus | Showy Aster
IMMEDIATE FIRE EFFECT ON PLANT : Showy aster is top-killed by fire. Because rhizomes often survive, the species has been classified as moderately resistant to fire [8]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Showy aster increases rapidly after fire [16,18]. Showy aster exhibits mass flowering in postfire years 1 and 2. The extent of flowering is directly related to preburn abundance and postfire survivorship [22,23,24]. Showy aster frequency increased from 8 percent before fire to 20 percent 2 years after a moderate-severity fire in a Douglas-fir forest in Idaho. By postfire year 7, showy aster frequency increased to 52 percent [16]. Following the 1977 Pattee Canyon Fire in Missoula, Montana, showy aster cover was 1.4 percent in 1978 and 2.0 percent in 1982 [16]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Aster conspicuus | Showy Aster
REFERENCES : 1. Arno, Stephen F.; Simmerman, Dennis G.; Keane, Robert E. 1985. Forest succession on four habitat types in western Montana. Gen. Tech. Rep. INT-177. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 74 p. [349] 2. 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] 3. Cole, David N. 1988. Disturbance and recovery of trampled montane grassland and forests in Montana. Res. Pap. INT-389. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 37 p. [3622] 4. Crane, M. F.; Fischer, William C. 1986. Fire ecology of the forest habitat types of central Idaho. Gen. Tech. Rep. INT-218. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 85 p. [5297] 5. Crane, M. F.; Habeck, James R.; Fischer, William C. 1983. Early postfire revegetation in a western Montana Douglas-fir forest. Res. Pap. INT-319. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 29 p. plus chart. [710] 6. 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] 7. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 8. Fischer, William C.; Bradley, Anne F. 1987. Fire ecology of western Montana forest habitat types. Gen. Tech. Rep. INT-223. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 95 p. [633] 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. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 11. Holcroft, Anne C.; Herrero, Stephen. 1991. Black bear, Ursus americanus, food habits in southwestern Alberta. Canadian Field-Naturalist. 105(3): 335-345. [18673] 12. Klinka, K.; Krajina, V. J.; Ceska, A.; Scagel, A. M. 1989. Indicator plants of coastal British Columbia. Vancouver, BC: University of British Columbia Press. 288 p. [10703] 13. 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] 14. Lackschewitz, Klaus. 1991. Vascular plants of west-central Montana--identification guidebook. Gen. Tech. Rep. INT-227. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 648 p. [13798] 15. Leege, Thomas A.; Herman, Daryl J.; Zamora, Benjamin. 1981. Effects of cattle grazing on mountain meadows in Idaho. Journal of Range Management. 34(4): 324-328. [2961] 16. Lyon, L. Jack. 1966. Initial vegetal development following prescribed burning of Douglas-fir in south-central Idaho. Res. Pap. INT-29. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 17 p. [1494] 17. Mace, Richard D. 1986. Analysis of grizzly bear habitat in the Bob Marshall Wilderness, Montana. In: Contreras, Glen P.; Evans, Keith E, compilers. Proceedings--grizzly bear habitat symposium; 1985 April 30 - May 2; Missoula, MT. Gen. Tech. Rep. INT-207. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 136-149. [10814] 18. McLean, Alastair. 1968. Fire resistance of forest species as influenced by root systems. Journal of Range Management. 22: 120-122. [1621] 19. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 20. Steele, Robert; Geier-Hayes, Kathleen. 1989. The Douglas-fir/ninebark habitat type in central Idaho: succession and management. Gen. Tech. Rep. INT-252. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 65 p. [8136] 21. Steele, Robert; Geier-Hayes, Kathleen. 1993. The Douglas-fir/pinegrass habitat type in central Idaho: succession and management. Gen. Tech. Rep. INT-298. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 83 p. [21512] 22. Stickney, Peter F. 1980. Data base for post-fire succession, first 6 to 9 years, in Montana larch-fir forests. Gen. Tech. Rep. INT-62. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 133 p. [6583] 23. Stickney, Peter. 1989. After forest wildfire, then what? .... Masses of flowers!. Words on Wilderness: The Newsletter of the Wilderness Studies Information Center. Missoula, MT: University of Montana: 6. [17441] 24. 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] 25. Tisdale, E. W.; McLean, A. 1957. The douglas-fir zone of southern interior British Columbia. Ecological Monographs. 27(3): 247-266. [8866] 26. 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] 27. Zimmerman, G. T.; Neuenschwander, L. F. 1984. Livestock grazing influences on community structure, fire intensity, and fire frequency within the Douglas-fir/ninebark habitat type. Journal of Range Management. 37(2): 104-110. [10103]

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