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Introductory

SPECIES: Yucca glauca | Soapweed Yucca
ABBREVIATION : YUCGLA SYNONYMS : Yucca angustifolia Yucca arkansana SCS PLANT CODE : YUGL YUGLG2 YUGLG COMMON NAMES : soapweed yucca soapwell beargrass Great Plains yucca soapweed small soapweed TAXONOMY : The currently accepted scientific name of soapweed yucca is Yucca glauca Nutt. [11,24]. Commonly recognized varieties are: Y. glauca var. glauca [11,24] Y. glauca var. mollis Engelm. [11,24] Y. glauca var. gurneyi McKelvey [24] Soapweed yucca hybridizes with Spaniah bayonet (Y. harrimaniae), Buckley's yucca (Y. constricta), Spanish dagger (Y. arizonica), Thompson's yucca (Y. thompsoniana), banana yucca (Y. baccata), soaptree yucca (Y. elata), narrowleaf yucca (Y. angustissima), and Bailey's yucca (Y. baileyi) [45,46]. Webber [45] refered to a swarm made up of soapweed yucca, narrowleaf yucca, Bailey's yucca, and Buckley's yucca, which is characterized by much interbreeding and plants with variable, intermediate morphological characteristics. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : Soapweed yucca is listed as vulnerable in Alberta and Saskatchewan [49]. COMPILED BY AND DATE : D. Tirmenstein, March, 1989. LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Tirmenstein, D. 1989. Yucca glauca. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Yucca glauca | Soapweed Yucca
GENERAL DISTRIBUTION : Soapweed yucca grows throughout much of the Great Plains from Texas and Arizona northward to Montana and the Dakotas [23,26]. It extends eastward into portions of Kansas, Nebraska, Iowa, and Missouri [23,45]. ECOSYSTEMS : FRES17 Elm - ash - cottonwood FRES21 Ponderosa pine FRES29 Sagebrush FRES31 Shinnery FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands STATES : AZ CO IA KS MO MT NE NM ND OK SD TX WY ADMINISTRATIVE UNITS : BADL BICA BUFF DETO FLFO GRSA ROMO SCBL THRO WICA BLM PHYSIOGRAPHIC REGIONS : 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 K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K023 Juniper - pinyon woodland K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K053 Grama - galleta steppe K054 Grama - tobosa prairie K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K059 Trans-Pecos shrub savanna K064 Grama - needlegrass - wheatgrass K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlegrass K070 Sandsage - bluestem prairie K071 Shinnery K098 Northern floodplain forest SAF COVER TYPES : 237 Interior ponderosa pine 239 Pinyon - juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Soapweed yucca is a common constituent of many plains grassland, drier forest-grassland and prairie communities. It has been described as a climax dominant on sandy range sites, and grasslands of Montana east of the Continental Divide [35]. It is listed as an indicator in the following range site classification scheme: Climax vegetation of Montana based on soils and climate [35] Associated plants: Soapweed yucca is commonly associated with the following species in plains grassland communities: needle-and-thread (Stipa comata), western wheatgrass (Pascopyrum (Agropyron) smithii), blue grama (Bouteloua gracilis), sand bluestem (Andropogon gerardii var. paucipilus), big bluestem (Andropogon gerardi var. gerardii), sideoats grama (B. curtipendula), little bluestem (Schizachyrium scoparium), sand dropseed (Sporobolus cryptandrus), galleta (Hilaria jamesii), mesquite (Prosopis glandulosa), sunflower (Helianthus spp.), and leadplant (Amorpha canescens) [3,10].

VALUE AND USE

SPECIES: Yucca glauca | Soapweed Yucca
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Soapweed yucca provides food and cover for a number of species throughout its wide range. Wild ungulates such as deer, bighorn sheep, and bison utilize this species to at least some degree. Generally, use by deer is fairly light, although Dusek [16] reported that soapweed yucca represented up to 20% of winter mule deer diets in portions of north-central Montana. Mule deer in this area also consumed smaller amounts of soapweed yucca during the spring and summer [16]. It has been used, generally in trace amounts, by bison on many shortgrass plains sites [31]. Research indicates that soapweed yucca is of greatest importance to bighorn sheep during late winter and early spring [40]. It is believed to represent an important and highly nutritious food source for bighorns during times of climatic stress. Cattle use of soapweed yucca appears to be fairly limited under normal conditions [18]. However, during drought periods in the Great Plains, cattle frequently consume flowers and succulent young leaves wherever available [13]. Soapweed yucca was chopped and fed as emergency silage to cattle during severe droughts in the early part of the century [13,45]. Little documentation exists on the specific value of soapweed yucca to domestic sheep and goats, although the leaves of many yuccas are readily eaten by goats [45]. The fruits and flowers of most yuccas are utilized by many small birds and mammals. PALATABILITY : Soapweed yucca appears to be relatively unpalatable to wild ungulates in most areas. Leaves become tough, and spiny as they mature. Younger, more succulent leaves, are much more palatable. However, during droughts, when other more palatable species are lacking, soapweed yucca may represent preferred forage. Soapweed yucca can be made palatable to domestic livestock, for use during drought emergencies, by burning off the older leaves and chopping the remainder of the plant for use as silage to be added to supplements such as cottonseed meal [45]. Flowers of soapweed yucca appear to be highly palatable to cattle [13], and presumably to most wild ungulates as well. The fruits of most yuccas are also palatable to a wide variety of birds and mammals. The relish and degree of use shown by livestock and wildlife species for soapweed yucca is rated as follows [14]: CO MT ND WY Cattle fair fair fair fair Sheep poor fair poor fair Horses fair fair fair fair Pronghorn ---- poor ---- fair Bighorn ---- ---- ---- ---- Elk ---- poor ---- fair Mt. goat ---- ---- ---- ---- Mule deer ---- good fair ---- White-tailed deer ---- ---- ---- good Small mammals ---- poor ---- poor Small nongame birds ---- poor ---- poor Upland game birds ---- poor ---- poor Waterfowl ---- ---- ---- ---- NUTRITIONAL VALUE : Soapweed yucca is rated as "poor" in overall energy and protein value [14]. The nutritional value of soapweed yucca varies seasonally as follows [6,20]: % composition Date moisture carotene ash crude crude crude fat protein fiber Jan.18 60.10 27.60 1.59 1.13 4.78 14.81 May 16 55.68 22.10 1.57 1.28 3.79 15.97 June27 64.71 18.04 1.87 .73 3.93 14.62 Oct 22 61.42 43.48 1.49 1.24 3.56 14.67 N-free extract Ca P Fe Mn Jan.18 17.59 .33 .100 40.76 23.20 May 16 21.53 .43 .070 67.31 16.54 June27 14.14 .31 .117 32.82 7.84 Oct 22 17.62 .28 .077 47.11 13.34 average % crude fiber ash protein leaf 42.3 4.86 5.57 COVER VALUE : Soapweed yucca provides good cover for a number of smaller birds and mammals. Studies indicate that soapweed yucca serves as good hiding cover for sharp-tailed grouse broods in North Dakota grasslands [22]. Scaled quail in southeastern New Mexico often incorporate soapweed yucca leaves in their nests which are frequently situated at the base of the plant [12]. Soapweed yucca provides the following environmental protection during one or more seasons for wildlife species in a number of western states [14]: CO MT ND WY Pronghorn ---- poor ---- fair Bighorn ---- ---- ---- ---- Elk ---- ---- ---- poor Mt. goat ---- ---- ---- ---- Mule deer ---- poor fair poor White-tailed deer ---- ---- ---- poor Small mammals ---- fair ---- poor Small nongame birds ---- fair ---- poor Upland game birds ---- poor ---- poor Waterfowl ---- ---- ---- poor VALUE FOR REHABILITATION OF DISTURBED SITES : Soapweed yucca is rated as having low value for short-term rehabilitation, and low to moderate value for use in long-term rehabilitation [14]. Plants may be transplanted or grown from seed. However, seedlings should be mulched in areas subject to winter frost [1]. Researchers note that soapweed yucca can be somewhat difficult to propagate [45]. OTHER USES AND VALUES : Many Native Americans historically used soapweed yucca for a variety of purposes. The saponin-rich roots were pulped to produce soap, thus giving this species its common name [47]. Fibers obtained from the leaves were fashioned into baskets, sandals, mats, and ropes [29]. During the early part of this century, soapweed yucca fiber was tested as a jute substitute in burlap products or cordage. High tensile strength (44.7 km), and clean, lustrous appearance made it well-suited for these uses [5,6]. During World War I, soapweed yucca was used to produce approximately 80 million pounds of fiber for bags and burlap [6]. This species was also used to make paper for the United States Navy during World War II [6,45]. Soapweed yucca is frequently planted as an ornamental [1]. MANAGEMENT CONSIDERATIONS : Chemical control: Soapweed yucca is resistant to the effects of herbicides. It is most susceptible during the bud stage, but only poor to fair control has been achieved [48]. Mechanical removal: A number of experiments have focused on mechanical removal or control of soapweed yucca. Researchers found that recovery in the number of leafheads is generally not achieved until the third year after treatment, although in some cases, recovery can occur within 3 months to 1 year. Recovery in the size (weight) of leafheads is generally much slower and requires 5 1/2 to 6 3/4 years [45]. Occasionally 2 or 3 new plants grow from each original plant [6]. Evidence suggests that season of treatment and weather conditions do not significantly influence the recovery of soapweed yucca although recovery may be slightly slower if plants are damaged late in the year. Some plants which had been cut at the soil surface produced inflorescences within only 23 to 36 months. Even successive removal or damage has failed to kill soapweed yucca. This resilient plant has continued to sprout for 3 years or more after deep seasonal plowing [45]. Productivity: Webber [45] reported average soapweed yucca yields of 0.2 to 0.8 ton per acre. Soapweed yucca is known to decrease in response to cattle grazing in parts of the Great Plains.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Yucca glauca | Soapweed Yucca
GENERAL BOTANICAL CHARACTERISTICS : Soapweed yucca is a small, acaulescent, perennial shrub which grows from 1 to 6 feet (.3-1.8 m) in height [1,45]. Plants are simple, or grow in dense clumps 2.6 to 8.2 feet (0.8-2.5 m) in diameter, with short often prostrate stems [23,45]. Soapweed yucca is typically deep-rooted [3], and long-lived. Researchers estimated that a plant 5 feet (1.5 m) in height was more than 50 years old [25]. The glaucous green leaves 1 to 3 feet (.3-1 m) in length are broad, stiff, and sharply pointed with fibrous margins [21,23,48]. The inflorescence is either racemose or paniculate, and up to .3 feet (1 m) in length on a 1 to 4 feet (.3-1.2 m) tall flowerstalk [23,47]. The flowers themselves are large, globose or campanulate and greenish-white with a purple tinge [21,45]. The oblong fruit develops into a woody capsule which contains numerous flat black, winged seeds [23,45,47]. RAUNKIAER LIFE FORM : Phanerophyte Geophyte REGENERATION PROCESSES : Soapweed yucca is capable of reproducing sexually or through vegetative means. Typically, rosettes grow for several years, bloom once and die, but are replaced by new rosettes derived vegetatively [28]. Winged seed is shiny, black, and averages .006 ounce (16 mg) in weight [2,23,27]. Seed is contained in a dehiscent, woody capsular fruit 2 to 3 inches (5-7 cm) long [23,26]. Plants generally first flower at 5 or 6 years of age [45]. Germination: Soapweed yucca seed may lack a mechanism for dormancy [28], and generally germinates well under favorable temperature and moisture conditions [27,41]. Germination rates range from 45 to 98% but generally average 80 to 90% under laboratory conditions [1]. However, Arnott [1] observed that only 20% of the seed actually produced viable seedlings in greenhouse experiments. Various treatments can influence germination. Without pretreatment, germination generally begins within 1 or 2 weeks [1]. Seed soaked in water for 24 hours often germinates within only 4 days [45]. Tolstead [41] reported that germination of untreated seeds averaged 67.1% while seed vernalized for 2 months averaged 86.6%. Germination may be adversely affected by exposure to heat as shown below [27]: % germination exposure time control 80 C 90 C 100 C 110 C 120 C 2 hours 79 57 42 -- -- -- 5 minutes -- -- 41 59 28 3 Pollination: One of the most interesting and well-studied aspects of yucca ecology centers around the symbiotic relationship between yuccas and their yucca moth pollinators. Soapweed yucca relies solely on the yucca moth (Tegeticula yuccasella) for pollination [36]. Seed production is thus totally dependent on the availability of this pollinator which, in the larval stage, feeds on a small percentage of seeds (generally around 7%) [26]. In some years, less than 1% of the racemes set fruit due to lack of pollinators, or poor weather conditions [28]. Vegetative regeneration: Evidence suggests that on newly disturbed sites, which lack competing grasses, soapweed yucca regenerates primarily from seed. Vegetative regeneration allow soapweed yucca to survive and expand on sites with significant competition such as prairie grasslands. On these sites a low ratio of seedlings to ramets is common [28]. Vegetative regeneration occurs through the sprouting of underground horizontal or oblique rhizomes which form a tangled network approximately 4-24 inches (10-60 cm) below the soil surface. Rhizomes are covered with a thick, rough, protective bark, branch and spread horizontally with vertical branches growing to the soil surface where new leafheads are formed. The connection to the mother plant gradually becomes less important with time and eventually dies [45]. Ramets are produced in late summer from lateral buds at the base of the inflorescence or from rhizomes near senescent rosettes. The basal diameter of individual rosettes is a good predictor of potential for vegetative regeneration, with larger rosettes exhibiting a much greater tendency to form new plants [28]. Soapweed yucca can resprout relatively quickly even after successive defoliations. There is little evidence to link season of injury or climatic factors with recovery [45]. SITE CHARACTERISTICS : Soapweed yucca grows on dry rocky outcrops, ridges, slopes, lower mountains, prairies, and plains [23,38,44,47]. It is often found thinly scattered in rolling grasslands or in open coniferous woodlands but also occurs in dense stands in some areas [21,45]. Soils: This yucca grows well on a variety of soils including coarse gravel, sand or porous loam [10,44]. Growth is ofen best on compact sands and soapweed yucca is frequently described as an indicator of sand [10]. Elevation: Generalized elevational ranges by state are as follows [14]: from: 4,000 to 9,500 ft (1,219-2,896 m) in CO 2,500 to 5,000 ft (762-1,524 m) in MT 3,800 to 6,400 ft (1,158-1,951 m) in WY SUCCESSIONAL STATUS : Soapweed yucca can occur as a colonizer on disturbed sites [28], or as a common climax dominant in a variety of plains grasslands, drier forest communities and prairies [34,35]. Seedlings often thrive on disturbed sites in which soil is exposed such as road cuts, overgrazed sites, or slide zones. However, small seedlings often compete poorly with grasses or older conspecifics. Existing plants or clones of this versatile plant can still increase in area through vegetative regeneration in grasslands or prairies. Interestingly, this yucca is described as both an increaser in response to grazing, and a climax species. Geographic variation in its reproductive modes and successional status is possible [28]. SEASONAL DEVELOPMENT : Soapweed yucca, unlike many of its plant associates, remains green throughout the winter months [16]. Lateral buds located at the base of the inflorescence produce new ramets during the late summer [28]. Flowering in this yucca typically occurs after a rosette has grown vegetatively for a number of years. The individual rosette dies after flowering but is replaced by new rosettes [28]. Generalized flowering dates are as follows [14]: location beginning of flowering end of flowering CO May July MT June July ND June July WY June July Fruit of soapweed yucca ripens during July and August, and seed is dispersed in September [1].

FIRE ECOLOGY

SPECIES: Yucca glauca | Soapweed Yucca
FIRE ECOLOGY OR ADAPTATIONS : Soapweed yucca is described as "extremely difficult to kill with fire" [38]. This species produces underground rhizomes which are presumably well-protected from the effects of heat by overlying soil and a thick, protective bark-like covering [45]. Seed germinates well [1] and seedlings establish readily on newly disturbed areas with little vegetation, such as recently burned sites. Certain extremely harsh, rocky sites may lack fuels necessary to sustain fire under ordinary circumstances. POSTFIRE REGENERATION STRATEGY : Rhizomatous shrub, rhizome in soil Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Yucca glauca | Soapweed Yucca
IMMEDIATE FIRE EFFECT ON PLANT : Precise effects may vary with season of burn, fire intensity and severity, and site characteristics. Postfire mortality of soapweed yucca has been reported [7,32,45]. However, many observers have noted that soapweed yucca is extremely difficult to kill with fire [38]. Morphologically similar species frequently survive and resprout even when all aboveground vegetation is consumed by fire. Soapweed yucca is rarely killed by other types of disturbance such as mechanical removal [45]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : This species is generally capable of regenerating through sprouting of underground rhizomes, located 4 to 24 inches (10-60 cm) beneath the surface [45], which are presumably somewhat protected from heat damage by overlying soil. Morphologically similar yuccas resprout prolifically after fire, and although vigorous sprouting has been observed following mechanical removal of soapweed yucca, a similar postfire response has not been widely reported in the literature. However, soapweed yucca has been observed to decrease in response to burning [7,32]. The protective bark which covers the rhizomes tends to thicken as plants age, and limited evidence suggests that older, larger plants are more likely to regenerate vegetatively [28]. Therefore, it is probable that older plants are more likely to sprout after fire. Additional research is needed to clarify the importance of such factors as fire intensity and severity, climate, soils, season of burn, and grazing history. Ecotypic or geographic variation is also possible. Recovery of soapweed yucca on d a site may be relatively rapid even where reestablishment occurs primarily through seed. Seeds germinate rapidly [1], and seedlings reportedly establish readily on newly disturbed sites which lack grasses or other competitors [28]. Maturation is rapid and flowering has been reported in plants as young as 5 or 6 years of age [45]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : The tender young shoots of soapweed yucca are highly palatable to livestock, particularly in drier years, and to rodents such as woodrats [13,45]. Postfire recovery may be poor where rodent numbers are unusually high [45]. In some areas, grazing must be limited to ensure good postfire recovery.

REFERENCES

SPECIES: Yucca glauca | Soapweed Yucca
REFERENCES : 1. Alexander, Robert R.; Pond, Floyd W. 1974. Yucca (L.) Yucca. In: Schopmeyer, C. S., ed. Seeds of woody plants in the United States. Agric. Handb. 450. Washington, DC: U.S. Department of Agriculture, Forest Service: 857-858. [7779] 2. Arnott, Howard J. 1962. The seed, germination, and seedling of yucca. Berkeley, CA: University of California Press. 96 p. [4317] 3. Barnes, P. W.; Harrison, A. T.; Heinisch, S. P. 1984. Vegetation patterns in relation to topography and edaphic variation in Nebraska Sandhills prairie. Prairie Naturalist. 16(4): 145-157. [396] 4. 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] 5. Botkin, C. W.; Shires, L. B. 1944. Tensile strength of yucca fibers. Technical Bulletin 316. Las Cruces, NM: New Mexico State University, Agricultural Experiment Station. 30 p. [4527] 6. Botkin, C. W.; Shires, L. B.; Smith, E. C. 1943. Fiber of native plants in New Mexico. Bulletin 300. Las Cruces, NM: New Mexico State University, Agricultural Experiment Station. 38 p. [5097] 7. Bragg, Thomas B. 1978. Effects of burning, cattle grazing, and topography on vegetation of the choppy sands range site in the Nebraska Sandhills Prairie. In: Hyder, Donald N., ed. Proceedings, 1st international rangeland congress; 1978 August 14-18; Denver, CO. Denver, CO: Society for Range Management: 248-253. [4468] 8. Brown, David E. 1982. Plains and Great Basin grasslands. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 115-121. [536] 9. Brutvan, B.; Klukas, R. (revised by R. Klukas). 1982. Checklist of plants of Wind Cave National Park.. [Place of publication unknown]: [Publisher unknown]. 32 p. On file with: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratoy, Missoula, MT. [374] 10. Costello, David F. 1944. Important species of the major forage types in Colorado and Wyoming. Ecological Monographs. 14: 107-134. [693] 11. Cronquist, Arthur; Holmgren, Arthur H.; Holmgren, Noel H.; [and others]. 1977. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 6. The Monocotyledons. New York: Columbia University Press. 584 p. [719] 12. Davis, C. A.; Sawyer, P. E.; Griffing, J. P.; Borden, B. D. 1974. Bird populations in a shrub-grassland area, southeastern New Mexico. Bulletin 619. Las Cruces, NM: New Mexico State University, Agricultural Experiment Station. 29 p. [4548] 13. Dayton, William A. 1931. Important western browse plants. Misc. Publ. 101. Washington, DC: U.S. Department of Agriculture. 214 p. [768] 14. 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] 15. Dorn, Robert D. 1977. Flora of the Black Hills. [Place of publication unknown]: Robert D. Dorn and Jane L. Dorn. 377 p. [820] 16. Dusek, Gary L. 1975. Range relations of mule deer and cattle in prairie habitat. Journal of Wildlife Management. 39(3): 605-616. [5938] 17. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 18. Frolik, A. L.; Shepherd, W. O. 1940. Vegetative composition and grazing capacity of a typical area of Nebraska sandhills rangeland. University of Nebraska Agricultural Experimental Station Research Bulletin. Number 117. 39 p. [5417] 19. 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] 20. Gastler, George F.; Moxon, Alvin L.; McKean, William T. 1951. Composition of some plants eaten by deer in the Black Hills of South Dakota. Journal of Wildlife Management. 15(4): 352-357. [3996] 21. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 22. Grosz, Kevin Lee. 1988. Sharp-tailed grouse nesting and brood rearing habitat in grazed and nongrazed treatments in southcentral North Dakota. Fargo, ND: North Dakota State University. 72 p. M.S. thesis. [5491] 23. Hitchcock, C. Leo; Cronquist, Arthur; Ownbey, Marion. 1969. Vascular plants of the Pacific Northwest. Part 1: Vascular cryptograms, gymnosperms, and monocotyledons. Seattle, WA: University of Washington Press. 914 p. [1169] 24. 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] 25. Kaul, Robert P.; Keeler, Kathleen H. 1980. Effects of grazing and juniper-canopy closure on the prairie flora in Nebraska high-plains canyons. In: Kucera, Clair L., ed. Proceedings, 7th North American prairie conference; 1980 August 4-6; Springfield, MO. Columbia, MO: University of Missouri: 95-105. [2923] 26. Keeley, Jon E.; Keeley, Sterling C.; Swift, Cheryl C.; Lee, Janet. 1984. Seed predation due to the yucca-moth symbiosis. American Midland Naturalist. 112(1): 187-191. [5808] 27. Keeley, Jon E.; Meyers, Adriene. 1985. Effect of heat on seed germination of southwestern Yucca species. Southwestern Naturalist. 30(2): 303-304. [5761] 28. Kingsolver, R. W. 1986. Vegetative reproduction as a stabilizing feature of the population dynamics of Yucca glauca. Oecologia. 69: 380-387. [4504] 29. Krochmal, A.; Paur, S.; Duisberg, P. 1954. Useful native plants in the American Southwestern deserts. Economic Botany. 8: 3-20. [2766] 30. 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] 31. Peden, D. G.; Van Dyne, G. M.; Rice, R. W.; Hansen, R. M. 1974. The trophic ecology of Bison bison L. on shortgrass plains. Journal of Applied Ecology. 11: 489-497. [1861] 32. Pool, Raymond J. 1914. A study of the vegetation of the sandhills of Nebraska. In: Minnesota Botanical Studies. Botanical Series VII. Minneapolis, MN: [University of Minnesota]: 189-312. [5891] 33. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 34. Renner, F. G.; Allred, B. W. 1962. Classifying rangeland for conservation planning. Agric. Handb. 235. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 48 p. [1956] 35. 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] 36. Schaffer, William M.; Schaffer, M. Valentine. 1979. The adaptive significance of variations in reproductive habit in the Agavaceae II: Pollinator foraging beh. and selection for increased reproductive expenditure. Ecology. 60(5): 1051-1069. [3061] 37. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. [23362] 38. Simpson, Philip George. 1975. Anatomy and morphology of the Joshua tree (Yucca brevifolia): an arborescent monocot. Santa Barbara, CA: University of California. 524 p. Dissertation. [6280] 39. 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] 40. Todd, J. W. 1975. Foods of Rocky Mountain bighorn sheep in southern Colorado. Journal of Wildlife Management. 39(1): 108-111. [6218] 41. Tolstead, W. L. 1941. Germination habits of certain sandhills plants in Nebraska. Ecology. 22: 393-397. [5020] 42. 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] 43. 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] 44. Weaver, J. E.; Albertson, F. W. 1956. Grasslands of the Great Plains. Lincoln, NE: Johnsen Publishing Company. 395 p. [2463] 45. Webber, John Milton. 1953. Yuccas of the Southwest. Agriculture Monograph No. 17. Washington, DC: U.S. Department of Agriculture, Forest Service. 97 p. [2474] 46. Webber, John M. 1960. Hybridization and instability of Yucca. Madrono. 15: 187-192. [5764] 47. Whitson, Tom D., ed. 1987. Weeds and poisonous plants of Wyoming and Utah. Res. Rep. 116-USU. Laramie, WY: University of Wyoming, College of Agriculture, Cooperative Extension Service. 281 p. [2939] 48. Wilson, R. G.; Martin, A. R.; Masters, R. A; [and others]. 1988. Chemical control of rangeland weeds. NebGuide G88-871. Cooperative Extension Service, Insitute of Agriculture and Natural Resources, University of Nebraska - Lincoln. [6816] 49. Committee on the Status of Endangered Wildlife in Canada. 1992. Canadian species at risk. Ottawa, ON. 10 p. [26183]

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Content on this web site is provided for informational purposes only. We accept no responsibility for any loss, injury or inconvenience sustained by any person resulting from information published on this site. We encourage you to verify any critical information with the relevant authorities.

Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

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