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Introductory

SPECIES: Arnica cordifolia | Heartleaf Arnica
ABBREVIATION : ARNCOR SYNONYMS : NO-ENTRY SCS PLANT CODE : ARCO9 COMMON NAMES : heartleaf arnica heart-leaved arnica TAXONOMY : The currently accepted scientific name of heartleaf arnica is Arnica cordifolia Hook. [15,34]. It is a member of the Asteraceae family. Recognized varieties are [21,29]: Arnica cordifolia var. cordifolia A. cordifolia var. pumila (Rydb.) Maquire 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. Arnica cordifolia. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Arnica cordifolia | Heartleaf Arnica
GENERAL DISTRIBUTION : Heartleaf arnica is found from Alaska east to Saskatchewan and south to northern Mexico and Nebraska [34,44]. A disjunct population occurs on the Keweenaw Peninsula of northern Michigan [18]. ECOSYSTEMS : FRES11 Spruce - fir FRES17 Elm - ash - cottonwood FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir - spruce FRES25 Larch FRES26 Lodgepole pine FRES28 Western hardwoods FRES29 Sagebrush FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES38 Plains grasslands FRES44 Alpine STATES : AL AZ CA CO ID MI MT NE NM ND OR SD UT WA WY AB BC SK YT MEXICO ADMINISTRATIVE UNITS : BIHO BICA BLCA BRCA CEBR CRLA CRMO DINO FOBU GLAC GRCA GRTE GRBA MORA NOCA OLYM ROMO TICA YELL YOSE ZION BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 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 13 Rocky Mountain Piedmont 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K007 Red fir forest K008 Lodgepole pine - subalpine forest K011 Western ponderosa forest K012 Douglas-fir forest K013 Cedar - hemlock - pine forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K021 Southwestern spruce - fir forest K023 Juniper - pinyon woodland K029 California mixed evergreen forest K037 Mountain-mahogany - oak scrub K052 Alpine meadows and barren K055 Sagebrush steppe K098 Northern floodplain forest SAF COVER TYPES : 201 White spruce 204 Black spruce 205 Mountain hemlock 206 Engelmann spruce - subalpine fir 207 Red fir 208 Whitebark pine 209 Bristlecone pine 256 California mixed subalpine 210 Interior Douglas-fir 211 White fir 212 Western larch 213 Grand fir 215 Western white pine 216 Blue spruce 217 Aspen 218 Lodgepole pine 219 Limber pine 224 Western hemlock 228 Western redcedar 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Heartleaf arnica is a dominant ground cover in many forest communities of the West. Publications listing heartleaf arnica as a dominant or indicator species are: Classification of the forest vegetation of Wyoming [1] Fire ecology of the forest habitat types of central Idaho [10] Forest vegetation of the Arapaho and Roosevelt National Forests in central Colorado: a habitat type classification [20] Forest vegetation of Bighorn Mountains, Wyoming: a habitat type classification [22] Plant associations of the Fremont National Forest [23] Forest vegetation of the Gunnison and parts of the Uncompahgre National Forests: a preliminary habitat type classification [26] Common plant associates of heartleaf arnica include huckleberry (Vaccinium spp.), sweetscented bedstraw (Galium triflorum), queencup beadlily (Clintonia uniflora), twinflower (Linnaea borealis), pussytoes (Antennaria spp.), timber milkvetch (Astragalus miser), elk sedge (Carex geyeri), and bluebunch wheatgrass (Pseudoroegneria spicata).

VALUE AND USE

SPECIES: Arnica cordifolia | Heartleaf Arnica
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : In northern Utah heartleaf arnica is an important constituent of summer diets of mule deer and elk [9]. Deschamps and Urness [12] found it comprised 24 percent of summer deer diets in mature lodgepole pine (Pinus contorta) forests in Utah. PALATABILITY : In Colorado, Montana, Utah, and Wyoming, the palatability of heartleaf arnica is rated poor to fair for cattle, fair to good for sheep, and poor for horses [13]. NUTRITIONAL VALUE : Heartleaf arnica is rated fair in nutritional value for pronghorn, upland game birds, small mammals, and small nongame mammals. It is rated fair to good in nutritional value for elk and deer [13]. COVER VALUE : Heartleaf arnica provides poor cover for wildlife [13]. VALUE FOR REHABILITATION OF DISTURBED SITES : Heartleaf arnica has low resistance to repeated human trampling [8,37]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Heartleaf arnica showed a substantial increase after heavy thinning of lodgepole pine stands in Utah. Production increased from 6.05 pounds per acre (1.1 kg/ha) before treatment to 83.6 pounds per acre (15.2 kg/ha) 4 years after treatment [2]. Heartleaf arnica cover increased from 0.3 percent to 5.0 percent following clearcutting in a subalpine forest in central Colorado [11].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Arnica cordifolia | Heartleaf Arnica
GENERAL BOTANICAL CHARACTERISTICS : Heartleaf arnica is a native, perennial herb 6 to 24 inches (15-60 cm) tall, with upright stems arising singly from long, slender, creeping rhizomes [18]. Rhizomes grow laterally 0.4 to 0.8 inches (1-2 cm) below the soil surface [7]. Root depths of 24 inches (60.9 cm) have been recorded in Montana [35]. The life span of heartleaf arnica is estimated at 12 years [6]. RAUNKIAER LIFE FORM : Geophyte REGENERATION PROCESSES : Sexual: Heartleaf arnica reproduces by wind-dispersed seed [6,7]. In central Idaho, Kramer and Johnson [27] found 25 percent of heartleaf arnica seed was in the upper 2 inches (5 cm) of soil, while 75 percent was 2 to 5 inches (5-10 cm) below the soil surface. Asexual: Heartleaf arnica sprouts from rhizomes [7,24,32]. SITE CHARACTERISTICS : Heartleaf arnica occurs in boreal and cool temperate climates. It is commonly found in open-canopy coniferous forests on high elevation water-shedding sites. It often inhabits exposed, moderately dry mineral soils, but occurs on a variety of soil types [25]. In California it is found from 3,500 to 10,000 feet (1,050-3,000 m), in dry to moist open or wooded places [33]. In Utah it is found from 5,000 to 11,000 feet (1,525-3,355 m) [44]. Occurrence increases with elevation. In the Madison Range of Montana it is the primary ground cover in subalpine fir (Abies lasiocarpa) forests above 9,000 feet (2,723 m) [36]. SUCCESSIONAL STATUS : Facultative Seral Species Heartleaf arnica is tolerant of both sun and shade, and may be present from initial to late seres [42,47]. Geier-Hayes found it increased the first 2 years following logging in a Douglas-fir/white spiraea (Pseudotsuga mensiesii/Spiraea betulifolia) habitat type in central Idaho [17]. This was probably due to mass flowering, which occurs 1 to 2 years after disturbance [41]. Heartleaf arnica importance apparently decreases within a few years after disturbance-induced mass flowering and increases again in later seres, possibly through vegetative reproduction. Steele and Geier-Hayes [46] found it reached highest coverage in late seral stages of the grand fir/globe huckleberry (Abies grandis/Vaccinium globulare) habitat type of central Idaho. It is a near-climax indicator of that habitat type. SEASONAL DEVELOPMENT : Heartleaf arnica flowers from May through August in California [33] and May through September in Colorado [13]. In Montana, flowering begins in early June, fruits ripen in mid-July, and seeds are dispersed at the end of July [40].

FIRE ECOLOGY

SPECIES: Arnica cordifolia | Heartleaf Arnica
FIRE ECOLOGY OR ADAPTATIONS : Heartleaf arnica is moderately fire resistant [31,37], typically sprouting from surviving rhizomes after fire [7,24,32]. It also regenerates from wind-dispersed seed [7,45], and from seed resulting from mass flowering at postfire year 1 or 2 [42]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Initial-offsite colonizer (off-site, initial community) Secondary colonizer - on-site seed

FIRE EFFECTS

SPECIES: Arnica cordifolia | Heartleaf Arnica
IMMEDIATE FIRE EFFECT ON PLANT : Heartleaf arnica is top-killed by fire. Rhizomes often survive. It is rated as susceptible [7,31] to intermediate [24] in resistance to fire damage. This probably varies according to how far below the soil surface rhizomes are buried. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Heartleaf arnica is apparently reduced by "high intensity" fires [24,30], but responds to "less intense" fires through rapid initial vegetative regrowth accompanied by heavy flowering and seedling establishment [24,42]. This is typically followed by a decline in cover and frequency within a few years [17]. Heartleaf arnica had the highest frequency and cover of all forbs 2 years following a severe fire (greater than 90 percent mortality of all trees) in a spruce-fir (Picea-Abies) ecosystem in Wyoming [3]. Frequency and cover values increased for 2 years following logging and broadcast burning in a Douglas-fir habitat type in Idaho. This trend was followed by a decline to 0 percent cover by postfire year 10 [17]. According to Barth, light, moisture, and soil depth are important factors determining the postfire density of heartleaf arnica [4]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

References for species: Arnica cordifolia


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3. Barmore, William J., Jr.; Taylor, Dale; Hayden, Peter. 1976. Ecological effects and biotic succession following the 1974 Waterfalls Canyon Fire in Grand Teton National Park. Research Progress Report 1974-1975. Unpublished report on file at: U.S. Department of Agriculture, Forest Service, Intermountain Fire Sciences Laboratory, Missoula, MT. 99 p. [16109]
4. Barth, Richard C. 1970. Revegetation after a subalpine wildfire. Fort Collins, CO: Colorado State University. 142 p. Thesis. [12458]
5. 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]
6. Bierzychudek, Paulette. 1982. Life histories and demography of shade-tolerant temperate forest herbs: a review. New Phytologist. 90: 757-776. [19197]
7. Bradley, Anne F.; Noste, Nonan V.; Fischer, William C. 1992. Fire ecology of forests and woodlands of Utah. Gen. Tech. Rep. INT-287. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 128 p. [18212]
8. 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]
9. Collins, William B.; Urness, Philip J. 1983. Feeding behavior and habitat selection of mule deer and elk on northern Utah summer range. Journal of Wildlife Management. 47(3): 646-663. [6915]
10. 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]
11. Crouch, Glenn L. 1985. Effects of clearcutting a subalpine forest in central Colorado on wildlife habitat. Res. Pap. RM-258. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 12 p. [8225]
12. Deschamp, Joseph A.; Urness, Philip J.; Austin, Dennis D. 1979. Summer diets of mule deer from lodgepole pine habitats. Journal of Wildlife Management. 43(1): 154-161. [4524]
13. 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]
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18. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603]
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20. Hess, Karl; Alexander, Robert R. 1986. Forest vegetation of the Arapaho and Roosevelt National Forests in central Colorado: a habitat type classification. Res. Pap. RM-266. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 48 p. [1141]
21. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168]
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40. Schmidt, Wyman C.; Lotan, James E. 1980. Phenology of common forest flora of the northern Rockies--1928 to 1937. Res. Pap. INT-259. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 20 p. [2082]
41. 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. 10 p. [20090]
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46. Steele, Robert; Geier-Hayes, Kathleen. 1987. The grand fir/blue huckleberry habitat type in central Idaho: succession and management. Gen. Tech. Rep. INT-228. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 66 p. [8133]
47. 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]


[8136] Index

Related categories for Species: Arnica cordifolia | Heartleaf Arnica

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