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Introductory

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
ABBREVIATION : OXYCAMC SYNONYMS : Oxytropis columbiana SCS PLANT CODE : OXCAC2 COMMON NAMES : Columbia River crazyweed TAXONOMY : The currently accepted scientific name of Columbia River crazyweed is Oxytropis campestris var. columbiana (St. John) Barneby. The variety has been recommended for elevation to species status [5]. As many as 10 varieties have been listed for O. campestris (yellow crazyweed), five of which have been recommended for elevation to species status [5,8]. LIFE FORM : Forb FEDERAL LEGAL STATUS : No special status OTHER STATUS : Montana Status: threatened USFS Region 1 Status: MT - sensitive Global Rank: GS - critically imperiled globally (5 or fewer occurrences) The Nature Conservancy ranks Columbia River crazyweed as apparently secure globally but critically imperiled in Montana [14] and Washington [17]. COMPILED BY AND DATE : Tara Y. Williams, October 1990 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Williams, Tara Y. 1990. Oxytropis campestris var. columbiana. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
GENERAL DISTRIBUTION : Columbia River crazyweed is endemic to the Columbia River basin in northeastern Washington but also occurs in northwestern Montana where it is found in the Flathead Lake region and along the North Fork of the Flathead River (Glacier National Park) [10]. Occurrence in Glacier National Park: Big Prairie along Inside Road, and Lone Pine Prairie along Mud Creek [10]. The species, Oxytropis campestris, is more or less circumboreal; montane to submontane in the Pacific Northwest. It occurs transcontinentally in Canada, south in the Rocky Mountains to Colorado and west to the Olympic Mountains [7]. ECOSYSTEMS : FRES36 Mountain grasslands FRES37 Mountain meadows STATES : MT WA ADMINISTRATIVE UNITS : GLAC BLM PHYSIOGRAPHIC REGIONS : 8 Northern Rocky Mountains KUCHLER PLANT ASSOCIATIONS : K050 Fescue - wheatgrass K051 Wheatgrass - bluegrass K063 Foothills prairie SAF COVER TYPES : NO-ENTRY SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : NO-ENTRY

VALUE AND USE

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Oxytropis species often contain toxic alkaloids which cause "loco" disease. The species is moderately tolerant of grazing, but it is generally avoided [15]. PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Yellow locoweed (Oxytropis campestris) has been recommended for use in revegetation of subalpine sites. At 2,350 feet (757 m) in Alaska, containerized seedlings showed 80 percent and 100 percent survival after one growing season with and without added topsoil [3]. The seed is easily collected but requires a lengthy dormancy and has a low germination rate (10%) [15]. Yellow locoweed is an excellent soil builder and has high erosion control capabilities. It fixes nitrogen and is very competitive on preferred sites. In northern areas (Alberta), it is resistant to northern diseases [15]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Columbia River crazyweed is threatened by agriculutral, recreational, residential, and dam development, and by invasion of woody species and exotic weeds onto grasslands.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
GENERAL BOTANICAL CHARACTERISTICS : Columbia River crazyweed is a native perennial forb with a heavy taproot and branched rootstocks. It has tufted basal leaves and grows 4 to 12 inches (10-30 cm) tall. The odd-pinnate leaves are 3 to 8 inches (8-20 cm) long. The flowers are zygomorphic and have a white corolla and a strongly purple-spotted keel. The pod is 0.5 to 1.5 inches (1-3 cm) long. There is a high root to shoot ratio [5,7,14,15]. The plant may fix nitrogen, but this has not been reported in the literature [4]. RAUNKIAER LIFE FORM : Hemicryptophyte REGENERATION PROCESSES : Columbia River crazyweed reproduces by seed produced by pollination and fertilization [15]. It is pollinated by bumblebee species with long tongues. No fruit was produced on flowers that were enclosed, but there was 96 percent fruit set on flowers under open pollination [1]. SITE CHARACTERISTICS : Columbia River crazyweed grows on rocky, gravelly, open or partially shaded areas in valleys. It has been reported at 2,900 to 3,500 feet (880-1,050 m) in northwestern Montana [14]. Yellow locoweed (Oxytropis campestris) grows best in sandy loam to clay loam soils. It is tolerant of moderately saline soils and low nutrient conditons but does not tolerate water-saturated soils such as heavy clay. It is drought tolerant but not at all tolerant of excessive shade [15]. Yellow locoweed grows in dry meadows and on debris accumulations, talus and scree slopes, boulder fell fields, and in areas with little soil and sparse vegetative cover [14]. SUCCESSIONAL STATUS : Yellow locoweed (O. campestris) was a pioneer on alkaline glacial outwash in Alsaka and in Alberta on a coal mine spoil exposed to severe wind and drought [15]. SEASONAL DEVELOPMENT : Columbia River crazyweed flowers from late June to early August [1].

FIRE ECOLOGY

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
FIRE ECOLOGY OR ADAPTATIONS : NO-ENTRY POSTFIRE REGENERATION STRATEGY : NO-ENTRY

FIRE EFFECTS

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
IMMEDIATE FIRE EFFECT ON PLANT : NO-ENTRY DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : NO-ENTRY DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Periodic burning may reduce competition from invading weeds and woody plants in crazyweed habitats [10].

REFERENCES

SPECIES: Oxytropis campestris var. columbiana | Columbia River Crazyweed
REFERENCES : 1. Bauer, Paul J. 1983. Bumblebee pollination relationships on the Beartooth Plateau tundra of southern Montana. American Journal of Botany. 70(1): 134-144. [12962] 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. Densmore, R. V.; Holmes, K. W. 1987. Assisted revegetation in Denali National Park, Alaska, U.S.A. Arctic and Alpine Research. 19(4): 544-548. [6078] 4. 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] 5. Elisens, Wayne J.; Packer, John G. 1980. A contribution to the taxonomy of the Oxytropis campestris complex in northwestern North America. Canadian Journal of Botany. 58: 1820-1831. [12963] 6. 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] 7. Hitchcock, C. Leo; Cronquist, Arthur. 1961. Vascular plants of the Pacific Northwest. Part 3: Saxifragaceae to Ericaceae. Seattle, WA: University of Washington Press. 614 p. [1167] 8. Kartesz, John T.; Kartesz, Rosemarie. 1980. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II: The biota of North America. Chapel Hill, NC: The University of North Carolina Press; in confederation with Anne H. Lindsey and C. Richie Bell, North Carolina Botanical Garden. 500 p. [6954] 9. 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] 10. Lesica, Peter. 1984. Rare vascular plants of Glacier National Park, Montana. Missoula, MT: University of Montana, Department of Botany. 27 p. [12049] 11. Lesica, P.; Moore, G.; Peterson, K. M.; Rumely, J. H. (Montana Rare Plant Project). 1984. Vascular plants of limited distribution in Montana. Monograph No. 2. Montana Academy of Sciences, Supplement to the Proceedings, Volume 43. Bozman, MT: Montana State University, Montana Academy of Sciences. 61 p. [11656] 12. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 13. Spence, John R.; Shaw, Richard J. 1981. A checklist of the alpine vascular flora of the Teton Range, Wyoming, with notes on biology and habitat preferences. Great Basin Naturalist. 41(2): 232-242. [9839] 14. U.S. Department of Agriculture, Forest Service, Northern Region. 1988. Sensitive plant field guide [Montana]. Missoula, MT. [12279] 15. Watson, L. E.; Parker, R. W.; Polster, D. F. 1980. Manual of plant species suitablity for reclamation in Alberta. Vol. 2. Forbs, shrubs and trees. Edmonton, AB: Land Conservation and Reclamation Council. 537 p. [8855] 16. 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] 17. Doren, Robert F.; Whiteaker, Louis D. 1991. The Exotic Pest Plant Council. Restoration & Management Notes. 9(1): 29-31. [15413]

Index

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