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Introductory

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
ABBREVIATION : ARTLUD SYNONYMS : Artemisia vulgaris var. ludoviciana Artemisia gnaphalodes SCS PLANT CODE : ARLU ARLUA ARLUC8 ARLUE ARLUI2 ARLUL2 ARLUM2 ARLUR ARLUS COMMON NAMES : Louisiana sagewort Louisiana sage Louisiana sagebrush cudweed sagebrush prairie sage western mugwort cudweed sagewort TAXONOMY : The fully documented scientific species name of Louisiana sagewort is Artemisia ludoviciana Nutt. This species complex contains much morphological and adaptive variation. Currently recognized subspecies are [30]: A. l. ssp. albula (Woot.) Keck white sagebrush A. l. ssp. canicans (Rybd.) Keck gray sagewort A. l. spp. estesii Chambers Estes' sagebrush A. l. ssp. incompta (Nutt.) Keck mountain sagewort A. l. ssp. ludoviciana foothill sagewort A. l. ssp. mexicana (Willd.) Keck Mexican white sagebrush A. l. ssp. redolens (Gray) Keck white dagebrush A. l. ssp. sulcata (Rydb.) Keck white sagebrush LIFE FORM : Forb FEDERAL LEGAL STATUS : See OTHER STATUS OTHER STATUS : A. l. ssp. estesii is federally listed as a Category 2 plant [32]. COMPILED BY AND DATE : N. McMurray, February 1987 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : McMurray, Nancy M. 1987. Artemisia ludoviciana. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
GENERAL DISTRIBUTION : Louisiana sagewort is distributed from northwestern Alberta and the Northwest Territories south through the Intermountain and Rocky Mountain regions to Mexico and east to Ontario, Illinois, and Arkansas. In the Pacific Northwest it is rarely found east of the Cascades. This species occurs from sagebrush plains to mountainous areas throughout the West and has been introduced into the eastern portion of the United States [4,8,9]. ECOSYSTEMS : FRES15 Oak - hickory FRES17 Elm - ash - cottonwood FRES20 Douglas-fir FRES21 Ponderosa pine FRES23 Fir - spruce FRES29 Sagebrush FRES30 Desert shrub FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands FRES44 Alpine STATES : AZ AR CA CO ID IL IN KS MN MO MT NE NV NM ND OK OR SD TX UT WA WI WY AB BC MB NT ON SK MEXICO ADMINISTRATIVE UNITS : AMIS ARCH BADL BAND BIBE BITH BICA BRCA CANY CARE CACA CHCU COLM CRMO DEVA DEWA DETO DINO EFMO FLFO FOBO FOBU GWCA GLAC GRCA GRTE GRKO GRBA GRSM GUMO JODA LAMR MEVE MOCA MORA MORU NABR ORPI PIPE ROMO SAGU THRO TICA WICA WUPA YELL YOSE ZION BLM PHYSIOGRAPHIC REGIONS : 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 : K011 Western ponderosa forest K012 Douglas-fir forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K021 Southwestern spruce - fir forest K023 Juniper - pinyon woodland K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K040 Saltbush - greasewood K051 Wheatgrass - bluegrass K052 Alpine meadows and barren K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K057 Galleta - threeawn shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlegrass K070 Sandsage - bluestem prairie K074 Bluestem prairie K075 Nebraska Sand Hills prairie K081 Oak savanna K098 Northern floodplain forest Disturbed SAF COVER TYPES : 206 Engelmann spruce - subalpine fir 210 Interior Douglas-fir 217 Aspen 219 Limber pine 237 Interior ponderosa pine 239 Pinyon - juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Louisiana sagewort is a minor seral species within a wide variety of nonforested and forested communities throughout the western United States. Mueggler and Stewart [18] report its presence in a number of grassland and shrubland habitat types in Montana, including those within the rough fescue (Festuca scabrella), Idaho fescue (F. idahoensis), bluebunch wheatgrass (Pseudoroegneria spicata), big sagebrush (Artemisia tridentata), and shrubby cinquefoil (Potentilla fruiticosa) series. In forested habitat types, it occurs as an understory species within the limber pine (Pinus flexilis), ponderosa pine (P. ponderosa), Douglas-fir (Pseudotsuga menziesii), and subalpine fir (Abies lasiocarpa) series [20].

VALUE AND USE

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Louisiana sagewort has limited value as a forage species. It may be of seasonal importance to domestic sheep, mule deer, elk, and other game animals [26,28] and is reported to be one of the most frequently utilized forbs by mule deer in the Rocky Mountains [14]. Plants probably receive select utilization during late fall and winter due to their location on exposed ridges and snow-free sites. Louisiana sagewort increases in response to grazing on rough fescue (Festuca scabrella) grassland habitat types in Montana [18]. PALATABILITY : Palatability of Louisiana sagewort generally decreases from north to south. In portions of Idaho and Utah it is an important domestic sheep browse during the fall and winter [27,28]. Large mammal utilization of Louisiana sagewort is primarily confined to green tissue [27]. Some forms produce large basal rosettes that remain green throughout most of the winter, but most of the stems and leaves typically die back to the ground following persistent frost, and this material does not cure well. The relish and degree of use shown by livestock and wildlife species for Louisiana sagewort in several western states is rated as follows [5]: CO MT ND UT WY Cattle Poor Poor Poor Fair Poor Sheep Fair Fair Fair Good Fair Horses Fair Poor Fair Poor Fair Pronghorn ---- Good Fair Fair Fair Elk ---- Fair ---- Fair Fair Mule deer ---- Fair Poor Fair Fair White-tailed deer ---- Poor Poor ---- Poor Small mammals ---- Fair ---- Fair Fair Small nongame birds ---- Fair ---- Fair Fair Upland game birds ---- Fair Poor Fair Fair Waterfowl ---- ---- ---- Poor Poor NUTRITIONAL VALUE : Louisiana sagewort is rated fair in energy and protein value [5]. COVER VALUE : The degree to which Louisiana sagewort provides environmental protection during one or more seasons for wildlife species is as follows [5]: MT ND UT WY Pronghorn ---- Fair Poor Poor Elk ---- ---- Poor Poor Mule deer ---- Poor Poor Poor White-tailed deer ---- Poor ---- Poor Small mammals Fair ---- Fair Fair Small nongame birds Fair ---- Fair Poor Upland game birds Fair Fair Fair Poor Waterfowl Poor ---- Poor Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Louisiana sagewort establishes and persists on severely disturbed sites throughout a wide range of plant communities. Plants spread rapidly by rhizomes, providing excellent soil cover and stabilization. Louisiana sagewort produced dense masses of rhizomes and fibrous roots the year following planting on sites in the Intermountain region [24]. It is able to tolerate moderate erosion. Once established, Lousiana sagewort serves as a nurse shrub [26]. Stranathan and Monsen [26] reported a cultivar, 'Summit' Louisiana sagewort, that is recommended for use on high-elevation disturbed sites. This cultivar has successfully established on sandy, blowout mine spoils at elevations above 7,500 feet (2,300 m). It can spread 78 inches (200 cm) within 5 years after planting on unstable, steep slopes. Further cultivar development is expected within the Louisiana sagewort complex. Louisiana sagewort is adapted for use in basin big sagebrush (A. tridentata ssp. tridentata), mountain big sagebrush (A. tridentata ssp. vaseyana), pinyon-juniper, mountain brush, aspen, and subalpine herbland communities [24]. It is also useful for riparian plantings in forested, mountain brush, and sagebrush-desert types [15,17]. Although it can be established via transplanting, direct seeding is the most practical method of plant establishment on large projects. Seeds are planted in the fall separately or in mixtures by drill, aerial, or broadcast seeding. Small seed size requires that special precautions be taken when using a standard drill operation. Stranathan and Mosen [26] recommend shallow planting depths at a rate of 0.25 pounds or less of seed per acre (280 g/ha); broadcast seeding should be followed by a light harrowing. OTHER USES AND VALUES : American Indians used Lousisana sagewort for ceremonial and purification purposes. Other historical uses include treating headaches, coughs, hemorrhoids, stomach disorders, and wounded horses. These highly aromatic plants were also made into pillows and saddlepads [27]. MANAGEMENT CONSIDERATIONS : NO-ENTRY

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
GENERAL BOTANICAL CHARACTERISTICS : Louisiana sagewort is a long-lived, fast growing, native, aromatic, suffruticose, perennial forb typically ranging in height from 11.7 to 39 inches (3 to 10 dm) [5,8,16]. Plants spread by rhizomes; stems are usually solitary or loosely clustered. This species exhibits wide ecotypic variation in stem height, leaf color and shape, seed production, and degree of rhizomatous spread [24]. Generally, alpine forms are somewhat more decumbent than the more erect, low elevation forms. Louisiana sagewort is extremely drought and cold tolerant. Although most plants die back to woody stem bases following frost, some forms are able to maintain green, basal rosettes until late winter, while other forms produce an abundance of fall sprouts [26]. The root system is quite extensive and consists of a coarse root mass located 1 to 4 inches (3 to 10 cm) below the soil surface. Nitrogen-fixing root nodules have been reported for this species; however, nodulation is somewhat inconsistent [7]. Stranathan and Mosen [26] indicate that Louisiana sagewort improves soil fertility and tilth. RAUNKIAER LIFE FORM : Chamaephyte REGENERATION PROCESSES : Louisiana sagewort employs both sexual and vegetative reproductive strategies. Numerous, wind-dispersed achenes are produced in the fall. Although seed production varies widely among ecotypes, most plants produce abundant seed from flowers which are either open or self-pollinated. Seeds are very small (approximately 3,800,000 per pound [8,360,000/kg]). Germination rate is often only 30 to 40 percent at purities of over 90 percent [26]. Most seed is dispersed within the first 7 days of seed maturity [9]. Seed heads mature quickly and shatter easily. Viability declines after more than 2 to 3 years in storage. Harvey [9] reported optimum germination temperatures of 70 to 73 degrees Fahrenheit (20-23 deg C), the highest optimum range of four Artemisia species compared. He suggested that this range may be an ecological adaptation to protect newly emerged seedlings from frost damage on lowland sites in Montana. Seedling mortality is quite high in nature, despite relatively rapid root elongation. Mean survival of seedlings on Montana study sites was approximately 1.2 percent. Data indicate that survival per 1,000 seedlings was only 0.07 percent. Plants produce seed within 3 years following establishment. Stranathan and Monsen [26] reported that plants produced seed within two growing seasons on irrigated seed plantations in Colorado. Louisiana sagewort regenerates vegetatively via rhizomes. The extensive root system is generally a dense, coarse root mass located from 1 to 4 inches (3 to 10 cm) below the soil surface. Harvey [6] reports sagewort colonies reaching diameters of 50 feet (15 m) on lowland sites in Montana, with annual radial increases averaging approximately 1.2 inches (3 cm). Efforts at age determination on these sites suggested larger colonies approaching 200 years of age or more. Research involving cultivar development in Louisiana sagewort indicates that rhizome expression is highly variable among ecotypes; some accessions are highly rhizomatous while others exhibit almost no evidence of rhizome initiation [9]. An accession selected for cultivar release spread approximately 78 inches (200 cm) within 5 years following planting on steep, unstble slopes in Colorado. On disturbed sites in Idaho, sprigged plants produced abundant rhizomes and fibrous roots during the 1st year [8]. SITE CHARACTERISTICS : Louisiana sagewort has a wide ecological amplitude and is able to occupy a diversity of sites throughout the western United States. Plants typically occur scattered on dry, open sites within grassland, shrubland, and forested communities. Although populations inhabit sites ranging in elevation from less than 3,000 feet (900 m) to more than 10,000 feet (3,000 m), subspecies gererally occupy rather distinct elevational regions. Artemisia ludoviciana ssp. ludoviciana is the most abundant and widespread; A. l. spp. incompta is restricted to alpine areas. Louisiana sagewort is adapted to a wide range of soil conditions including heavy clays, sterile sands, and granitics. Productive sites in Montana are often along lowland, cold air drainages; colonal increases appear to be more rapid on mesic sites [9]. Elevational ranges for several western states are as follows [5]. 3,500 to 11,300 ft (1,067 to 3,455 m) in CO 2,300 to 9,200 ft (701 to 2,805 m) in MT 4,000 to 11,500 ft (1,220 to 3,506 m) in UT 3,600 to 10,900 ft (1,098 to 3,323 m) in WY SUCCESSIONAL STATUS : Facultative Seral Species Louisiana sagewort is a pioneer species that rapidly invades disturbed sites in a variety of plant communities. These long-lived plants establish during early seral conditions and coexist with later arriving species, often persisting through a wide range of successional stages. Although frequencies are typically low on most sites, densities increase where disturbance results in reduced species competition. Louisiana sagewort serves as a nurse shrub; grasses invaded plantings within 2 to 5 years on sites in Colorado [26]. As succession proceeds, sagewort densities gradually diminish; however, remnant plants will reemerge to occupy vegetative openings. SEASONAL DEVELOPMENT : Phenological development in Louisiana sagewort has not been well documented. Detailed data from Montana for sites below 5,900 feet (1,800 m) are presented below. In general, plants above this elevation developed 2 to 3 weeks later [9]. Phenological stage Month apical bud enlargement early to mid-April apical twig elongation mid-April to mid-May apical growth ceases (vegetative) mid-May to early-June floral branch elongation June floral buds enlarging July anther development (buds yellow) early to mid-August anthesis mid-August to mid-September cypsella (fruit) development mid-September to mid-October dissemination initiated mid-October to early November dissemination completed mid-November to mid-December winter dormancy mid-December to March

FIRE ECOLOGY

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
FIRE ECOLOGY OR ADAPTATIONS : The effects of fire on Louisiana sagewort is not well documented. Although plants are readily top-killed by all fire intensities, these suffrutescent perennials appear moderately resistent to fire mortality [1,2]. Generalized information indicates that plants are able to reestablish rapidly via rhizomes and perhaps through basal sprouting. Postfire regeneration also involves the germination of numerous wind-dispersed seeds [12,29]. POSTFIRE REGENERATION STRATEGY : Rhizomatous shrub, rhizome in soil Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
IMMEDIATE FIRE EFFECT ON PLANT : Louisiana sagewort is apparently easily top-killed by low intensity fires. The presence of underground rhizomes and suffrutescent stem bases suggests that the majority of plants are somewhat resistant to fire mortality [1,2]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Limited fire response data for Louisiana sagewort indicates that densities are rapidly regained and usually enhanced following burning. Plants spread rapidly via surviving rhizomes. Plant establishment also occurs from off-site seed sources. Studies in Alberta indicated that this species is well adapted to repeated, annual spring burning [1]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Artemisia ludoviciana | Louisiana Sagewort
REFERENCES : 1. Anderson, Howard G.; Bailey, Arthur W. 1980. Effects of annual burning on grassland in the aspen parkland of east-central Alberta. Canadian Journal of Botany. 58: 985-996. [3499] 2. Bailey, Arthur W.; Anderson, Murray L. 1978. Prescribed burning of a Festuca-Stipa grassland. Journal of Range Management. 31: 446-449. [373] 3. 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] 4. Cronquist, Arthur. 1955. Vascular plants of the Pacific Northwest: Part 5: Compositae. Seattle: University of Washington Press. 343 p. [716] 5. 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] 6. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 7. Grime, J. P. 1979. Plant strategies & vegetation proceses. Chichester, England: John Wiley & Sons. 222 p. [2896] 8. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 9. Harvey, A. D. 1936. Rootsprouts as a means of vegetative reproduction in Opuntia polyacantha. Journal of the American Society of Agronomy. 28: 767-768. [1101] 10. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 11. Holmgren, Arthur H.; Reveal, James L. 1966. Checklist of the vascular plants of the Intermountain Region. Res. Pap. INT-32. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 160 p. [1184] 12. Johnson, A. H.; Strang, R. M. 1983. Burning in a bunchgrass/sagebrush community: the southern interior of B.C. and northwestern U.S. compared. Journal of Range Management. 36(5): 616-618. [1273] 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. 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] 15. McArthur, E. Durant. 1983. Taxonomy, origin and distribution of big sagebrush ( Artemisia tridentata) and allies (subgenus Tridentatae). In: Johnson, Kendall L., ed. Proceedings--first Utah shrub ecology workshop; 1981 September 9-10; Ephraim, UT. Logan, UT: Utah State University: 3-14. [1566] 16. McArthur, E. Durant; Welch, Bruce L.; Nelson, David L. 1985. Developing improved cultivars of sagebrushes and other composite shrubs. In: Carlson, Jack R.; McArthur, E. Durant, chairmen. Range plant improvement in western North America: Proceedings of a symposium at the annual meeting of the Society for Range Management; 1985 February 14; Salt Lake City, UT. Denver, CO: Society for Range Management: 80-88. [1581] 17. Monsen, Stephen B. 1983. Plants for revegetation of riparian sites within the Intermountain region. In: Monsen, Stephen B.; Shaw, Nancy, compilers. Managing Intermountain rangelands--improvement of range and wildlife habitats: Proceedings 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: 83-89. [9652] 18. 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] 19. Noble, I. R.; Slatyer, R. O. 1977. Post-fire succession of plants in Mediterranean ecosystems. In: Mooney, Harold A.; Conrad, C. Eugene, tech coords. Proc. of the symp. on the environmental consequences of fire and fuel management in Mediterranean ecosystems; 1977 August 1-5; Palo Alto, CA. Gen. Tech. Rep. WO-3. Washington, DC: U.S. Department of Agriculture, Forest Service: 27-36. [1766] 20. Pfister, Robert D.; Kovalchik, Bernard L.; Arno, Stephen F.; Presby, Richard C. 1977. Forest habitat types of Montana. Gen. Tech. Rep. INT-34. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 174 p. [1878] 21. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 22. Ross, Robert L.; Hunter, Harold E. 1976. Climax vegetation of Montana based on soils and climate. Bozeman, MT: U.S. Department of Agriculture, Soil Conservation Service. 64 p. [2028] 23. Rowe, J. S. 1983. Concepts of fire effects on plant individuals and species. In: Wein, Ross W.; MacLean, David A., eds. SCOPE 18: The role of fire in northern circumpolar ecosystems. Chichester; New York: John Wiley & Sons: 135-154. [2038] 24. Shaw, Nancy L.; Monsen, Stephen B. 1983. Phenology and growth habits of nine antelope bitterbrush, desert bitterbrush, Stansbury cliffrose, and Apache-plume accessions. In: Tiedemann, Arthur R.; Johnson, Kendall L., compilers. Proceedings--research and management of bitterbrush and cliffrose in western North America; 1982 April 13-15; Salt Lake City, UT. Gen. Tech. Rep. INT-152. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 55-69. [2122] 25. 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] 26. Stranathan, Sam E.; Monsen, Stephen B. 1986. Selection of a cultivar of Artemisia ludoviciana for disturbed land plantings. In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium of the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 108-113. [2263] 27. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 28. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 29. Wright, Henry A. 1985. Effects of fire on grasses and forbs in sagebrush-grass communities. 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 Management, Idaho State Office: 12-21. [2617] 30. Kartesz, John T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II--thesaurus. 2nd ed. Portland, OR: Timber Press. 816 p. [23878] 31. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. [23104] 32. U.S. Department of the Interior, Fish and Wildlife Service. 1993. 50 CFR Part 17: Plant taxa for listing as endangered or threatened species; notice of review--September 30, 1993. Federal Register. 58(188): 51144-51190. [23816] 33. U.S. Department of the Interior, National Biological Survey. [n.d.]. NP Flora [Data base]. Davis, CA: U.S. Department of the Interior, National Biological Survey. [23119]

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