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Introductory

SPECIES: Asarum caudatum | Wild Ginger
ABBREVIATION : ASACAU SYNONYMS : Asarum caudatum var. viridifolum M.E. Peck SCS PLANT CODE : ASCA2 COMMON NAMES : wild ginger British Columbia wild ginger TAXONOMY : The currently accepted scientific name for wild ginger is Asarum caudatum Lindley [20]. It is a member of the Birthwort family, Aristolochiaceae [14]. LIFE FORM : Forb FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Mary Lou Zimmerman, May 1991 LAST REVISED BY AND DATE : Griffith, Randy Scott, June 1991. AUTHORSHIP AND CITATION : Zimmerman, Mary Lou; Griffith, Randy Scott. June 1991. Asarum caudatum. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Asarum caudatum | Wild Ginger
GENERAL DISTRIBUTION : Wild ginger occurs in California, Oregon, Washington, British Columbia, Idaho, and Montana [9]. In California it occurs in the Coast Ranges from the Santa Cruz Mountains northward [14]. In Oregon, Washington, and British Columbia, it is commonly found from the Pacific Coast east to the Cascades and is found less frequently on the east side of the Cascades. Wild ginger is also found in northern Idaho and western Montana [9]. ECOSYSTEMS : FRES20 Douglas-fir FRES22 Western white pine FRES23 Fir - spruce FRES24 Hemlock - Sitka spruce FRES25 Larch FRES27 Redwood FRES28 Western hardwoods STATES : CA ID MT OR WA BC ADMINISTRATIVE UNITS : CRLA MORA NOCA OLYM PORE REDW BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 3 Southern Pacific Border 8 Northern Rocky Mountains KUCHLER PLANT ASSOCIATIONS : K001 Spruce - cedar - hemlock forest K002 Cedar - hemlock - Douglas-fir forest K003 Silver fir - Douglas-fir forest K004 Fir - hemlock - Douglas-fir forest K005 Mixed conifer forest K006 Redwood forest K007 Red fir forest K012 Douglas-fir forest K013 Cedar - hemlock - pine forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest SAF COVER TYPES : 201 White spruce 206 Engelmann spruce - subalpine fir 210 Interior Douglas-fir 212 Western larch 213 Grand fir 215 Western white pine 221 Red alder 223 Sitka spruce 224 Western hemlock 225 Western hemlock - Sitka spruce 226 Coastal true fir - hemlock 227 Western redcedar - western hemlock 228 Western redcedar 229 Pacific Douglas-fir 230 Douglas-fir - western hemlock 232 Redwood 234 Douglas-fir - tanoak - Pacific madrone SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Wild ginger is commonly found in the understory of grand fir (Abies grandis), western white pine (Pinus monticola), Douglas-fir (Pseudotsuga menziesii), western redcedar (Thuja plicata), and western hemlock (Tsuga heterophylla). In the understory community, wild ginger is commonly associated with trail plant (Adenocaulon bicolor), queencup beadlily (Clintonia uniflora), and western goldthread (Coptis occidentalis) [2]. Wild ginger is listed as an indicator or dominant in the following habitat type (hts) and community type (cts) classifications: Location Classification Authority n-c ID forest cts Pierce and Peek 1984 n ID forest hts,cts Cooper et al 1987

VALUE AND USE

SPECIES: Asarum caudatum | Wild Ginger
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : Food: The roots and new shoots can be baked or roasted, then eaten. The leaves can be used to cover various foods while baking. The roots can be dried and used for seasoning [5]. Landscaping: Wild ginger is a favorite of native plant gardeners in the Pacific Northwest. It is considered high garden quality due to its characteristic showy heart-shaped leaves, aroma, ease of growth, and ability to form a dense carpet [9]. MANAGEMENT CONSIDERATIONS : Wild ginger will disappear from sites in the more xeric portions of its range that have been opened up by clearcutting. Large openings made in the forest canopy by clearcutting cause an increase in air and soil temperatures, evaporation rates, and moisture deficits, which present unfavorable conditions for reestablishment of moisture-loving plants, such as wild ginger [11].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Asarum caudatum | Wild Ginger
GENERAL BOTANICAL CHARACTERISTICS : Wild ginger is a low, trailing, perennial, evergreen, prostrate herb which is often found in localized patches on the forest floor. Its leaves are softly hairy, borne two per node, alternate, simple, appearing basal, long petioled, heart shaped, persistent, prominently veined, entire edged, aromatic, dark to bright green, and sometimes mottled. Its large, solitary, thimblelike flowers grow close to the ground and are often concealed by the leaves. They are brownish-purple to green and have three broad lobes which taper into long linear tails. The fruit is a large, fleshy capsule containing small seeds. The seeds are angled or compressed, smooth or wrinkled, and have a minute embryo in a fleshy endosperm. They are widely distributed. The roots of wild ginger are rhizomatous. They are extensive, slender, elongate, aromatic, and can become matted. [5,6,9,14]. RAUNKIAER LIFE FORM : Chamaephyte REGENERATION PROCESSES : Sexual: Wild ginger reproduces sexually by seed [9]. Vegetative: Wild ginger spreads by a system of extensive rhizomes. It may form localized patches [9]. SITE CHARACTERISTICS : Wild ginger is an indicator of moist, shady, lowland to midmontane forests in Oregon, Washington, and coastal British Columbia [5,8]. Soil: Wild ginger is characteristic of Moder and Mull humus soil forms [8]. Climate: Wild ginger is found in areas with cool temperate and cool mesothermal climates [8]. In northern Idaho and British Columbia the climate is an inland expression of the Pacific Maritime influence [15]. This plant prefers locations with moist weather in the fall, winter, and spring with dry summers [15]. Elevation: Wild ginger generally occurs below 5,000 feet (1,524 m) [2,14]. SUCCESSIONAL STATUS : Wild ginger is shade tolerant [8]. SEASONAL DEVELOPMENT : Wild ginger flowers from May through July in California [14], and from April through July in Oregon and Washington [5].

FIRE ECOLOGY

SPECIES: Asarum caudatum | Wild Ginger
FIRE ECOLOGY OR ADAPTATIONS : In Moder and Mull soil types the organic layers (L,F, and H) are typically shallow [7]. Therefore, a fire of light to moderate intensity would remove the organic layers and the vegetative propagules of wild ginger, thus requiring it to be seeded on the site from an off-site source [18]. POSTFIRE REGENERATION STRATEGY : Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Asarum caudatum | Wild Ginger
IMMEDIATE FIRE EFFECT ON PLANT : Wild ginger is very susceptible to fire-kill. Above and belowground parts can be killed by fires of even light to moderate intensity. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Wild ginger is removed from the understory until it can be seeded onto the site from an off-site source after fires of light to moderate intensity. Studies in Idaho and Oregon found that wild ginger presence was significantly higher in plots that were clearcut and not burned than in those plots that were clearcut and then broadcast burned [13,19]. Steen [19] found that wild ginger was absent from the burned stands for up to 16 years after slash fires of moderate intensity. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Wild ginger did not occur on clearcut and burned plots but did occur on clearcut and unburned plots in an Oregon study [19].

REFERENCES

SPECIES: Asarum caudatum | Wild Ginger
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. Cooper, Stephen V.; Neiman, Kenneth E.; Steele, Robert; Roberts, David W. 1987. Forest habitat types of northern Idaho: a second approximation. Gen. Tech. Rep. INT-236. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 135 p. [867] 3. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 4. 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] 5. Halverson, Nancy M., compiler. 1986. Major indicator shrubs and herbs on National Forests of western Oregon and southwestern Washington. R6-TM-229. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 180 p. [3233] 6. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 7. Kimmins, J. P. 1987. Forest ecology. New York: Macmillan Publishing Co. 531 p. [14184] 8. 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] 9. Kruckeberg, A. R. 1982. Gardening with native plants of the Pacific Northwest. Seattle: University of Washington Press. 252 p. [9980] 10. 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] 11. Larsen, J. A. 1924. Some factors affecting reproduction after logging in northern Idaho. Journal of Agricultural Research. 28(11): 1149-1157. [12934] 12. 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] 13. Mueggler, W. F. 1961. Ecology of seral shrub communities in the cedar-hemlock zone of northern Idaho. Durham, NC: Duke University. 126 p. Thesis. [9981] 14. Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA: University of California Press. 1905 p. [6155] 15. Neiman, K. E., Jr. 1988. Synecology of western redcedar in the northern rocky mountains. In: Smith, N. J., ed. Western red cedar--does it have a future?; [Date of conference unknown]; [Location of conference unknown]. Vancouver, BC: University of British Columbia, Faculty of Forestry: 114-121. [6704] 16. Pierce, D. John; Peek, James M. 1984. Moose habitat use and selection patterns in north-central Idaho. Journal of Wildlife Management. 48(4): 1334-1343. [12516] 17. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 18. Ryan, Kevin C.; Noste, Nonan V. 1985. Evaluating prescribed fires. In: Lotan, James E.; Kilgore, Bruce M.; Fischer, William C.; Mutch, Robert W., technical coordinators. Proceedings--symposium and workshop on wilderness fire; 1983 November 15-18; Missoula, MT. Gen. Tech. Rep. INT-182. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 230-238. [12456] 20. 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]

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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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