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Introductory

SPECIES: Bouteloua gracilis | Blue Grama
ABBREVIATION : BOUGRA SYNONYMS : Chondrosium gracile Actinochloa gracilis Eutriana gracilis Atheropogon gracilis Atheropogon oligostachyus Eutriana oligostachya Chondrosium oligostachyum Bouteloua oligostachya SCS PLANT CODE : BOGR2 COMMON NAMES : blue grama narajita azul white grama red grama purple grama TAXONOMY : The currently accepted scientific name of blue grama is Bouteloua gracilis (H.B.K.) Lag. ex Steud. Hitchcock [24] lists one variety: Bouteloua gracilis var. stricta (Vasey) Hitchc. This variety is distinguished by four to six ascending to appressed spikes [24]. LIFE FORM : Graminoid FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : D. Tirmenstein, June 1987 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Tirmenstein, D, A. 1987. Bouteloua gracilis. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Bouteloua gracilis | Blue Grama
GENERAL DISTRIBUTION : Blue grama is a major component of the shortgrass prairie and occurs throughout the Great Plains. It is distributed from Canada to Mexico, and from California eastward to the Atlantic Coast [24]. Blue grama has been introduced in many locations in the eastern United States [24]. ECOSYSTEMS : FRES21 Ponderosa pine FRES35 Pinyon - juniper FRES38 Plains grasslands FRES39 Prairie STATES : AZ AR CA CO DE HI ID IL IN IA KS KY ME MD MI MN MO MT NE NV NH NM NY NC ND OH OK PA SD TN TX UT VT VA WV WI WY AB BC LB MB NB NF NS ON PE PQ NT SK Mexico ADMINISTRATIVE UNITS : AGFO BADL BIBE BICA BRCA CACH CANY CARE CACA CHCU CHIR COLM CORO DETO DINO FLFO FOBO GLAC GLCA GRSA GUMO JECA LAMR MEVE NABR PEFO PIPE ROMO SCBL SUCR THRO WACA WHSA WICA WUPA YELL ZION BLM PHYSIOGRAPHIC REGIONS : 3 Southern Pacific Border 6 Upper Basin and Range 7 Lower Basin and Range 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 K031 Oak - juniper woodlands K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K039 Blackbrush K040 Saltbush - greasewood K041 Creosotebush K053 Grama - galleta steppe K054 Grama - tobosa prairie K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K057 Galleta - threeawn shrubsteppe K058 Grama - tobosa shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - needlegrass K068 Wheatgrass - grama - buffalo grass K069 Bluestem - grama prairie K070 Sandsage - bluestem prairie K071 Shinnery K074 Bluestem prairie K075 Nebraska sandhills prairie K081 Oak savanna K098 Northern floodplain forest SAF COVER TYPES : 206 Engelmann spruce - subalpine fir 210 Interior Douglas-fir 220 Rocky Mountain juniper 236 Bur oak 237 Interior ponderosa pine 239 Pinyon - juniper 241 Western live oak SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Blue grama is a climax indicator in many grassland, sagebrush, desert shrub, pinyon-juniper, and ponderosa pine communities and habitat types. It is associated with a variety of species including one-seed juniper (Juniperus monosperma), big sagebrush (Artemisia tridentata), broom snakeweed (Gutierrezia sarothrae), galleta (Hilaria jamesii), dropseed (Sporobolus spp.), western wheatgrass (Pascopyrum smithii), bluebunch wheatgrass (Pseudoroegneria spicata), buffalo grass (Buchloe dactyloides), needle-and-thread (Stipa comata), sand bluestem (Andropogon gerardii var. paucipilus), and big bluestem (Andropogon gerardi var. gerardii). Classifications listing blue grama as an indicator or dominant species in habitat, vegetation, or community typings are as follows: A classification of forest habitat types of northern New Mexico and southern Colorado [12] Phyto-edaphic communities of the Upper Rio Puerco Watershed, New Mexico [17] Preliminary habitat types of a semiarid grassland [18] A habitat type classification system for ponderosa pine forests of northern Arizona [22] Plant assocatitions of Region 2: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas [28] A habitat type classification of the pinyon-juniper woodlands of the Lincoln National Forest, New Mexico [29] A series vegetation classification for Region 3 [33]

VALUE AND USE

SPECIES: Bouteloua gracilis | Blue Grama
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Wildlife and all classes of livestock graze blue grama [4]. The species has relatively low productivity because of its short growth form [51]. Growth begins in May or June, so blue grama provides little or no green forage in the spring and early summer when foliage is scarce [47]. Although food value declines when the foliage is mature and dry [41], it is still consumed and provides good fall and winter forage [47,51]. Blue grama is very tolerant of grazing and trampling [5]. It has increased on many overgrazed ranges [47]. Large herbivores consume spikelets throughout the year and disseminate seed widely [54]. Adaptative traits such as extreme resistance to grazing and seed dispersal mechanisms suggest that this species has coevolved with large herbivores. Many species of small birds and mammals consume blue grama seeds [49]. PALATABILITY : Blue grama is highly palatable to many species of wildlife and all classes of livestock. It remains palatable during the fall and winter when the plant is mature and dried [51]. Bison in Oklahoma prefer it [39]. In some areas, domestic sheep graze it preferentially [41]. Pronghorn graze blue grama sparingly [49]. Blue grama is heavily used by many species of small rodents [47]. It is an important food of the northern pocket gopher during June, when it shows maximum growth [48]. It is relatively unpalatable to them the rest of the the year [48]. The degree of use shown by livestock and wildlife species for blue grama in several western states is rated as follows [13]: CO MT ND UT WY Cattle Good Good Good Good Good Sheep Good Good Good Good Good Horses Good Good Good Good Good Pronghorn ---- Poor Poor Fair Fair Elk ---- Poor ---- Fair Fair Mule deer ---- Poor Poor Fair Poor White-tailed deer ---- ---- Poor ---- Poor Small mammals ---- ---- Good Good Poor Small nongame birds ---- ---- ---- Good Poor Upland game birds ---- ---- ---- Fair Poor Waterfowl ---- ---- Fair Poor Poor NUTRITIONAL VALUE : Blue grama is rated fair in protein and energy value [13]. In a Wyoming study, blue grama magnesium and calcium levels decreased throughout the growing season, and the plant was deficient in phosphorous by mid-August [41]. By September, it had lost more than 46 percent of the original crude protein content. By end of October, it had lost 66 percent [41]. With fall rains and renewed growth, the decline of calcium and magnesium stopped and protein content increased. Frequent defoliation of blue grama during the growing season had little effect on total carbohydrate reserves or nonstructural carbohydrates [7]. Blue grama nutritional values as established by the National Academy of Sciences [36] are as follows: Aerial Hay Aerial Aerial Aerial Part Early Part Part Part Fresh Bloom Fresh Fresh Fresh Weathered Immature Mature Dormant Mature Ash % 7.9 12.0 11.1 14.2 19.6 Crude Fiber 38.6 30.1 28.7 30.0 39.7 Ether Extract % 1.1 2.2 1.8 1.7 2.7 N-free Extract % 48.9 44.4 46.9 46.2 31.7 Protein (Nx6.25) % 3.5 11.3 11.5 7.9 6.3 Dig.Protein-cattle % 0.0 6.7 7.7 4.6 3.2 Dig.Protein-horses % 0.5 7.1 7.3 4.2 2.9 Dig.Protein-sheep % 0.2 7.1 7.7 4.4 2.9 Ca % 0.28 6.7 0.40 --- --- P % 0.07 --- 0.16 --- --- COVER VALUE : Blue grama provides poor cover for small mammals, upland game birds, and waterfowl [13]. VALUE FOR REHABILITATION OF DISTURBED SITES : Blue grama is well adapted for use in revegetating drier parts of the central Great Plains [55]. Once established, it is persistent and productive; it serves as a soil binder and helps prevent erosion [47]. Seedling establishment can, however, be difficult due to low seed weight, the potential for only one seminal root, and limited capacity for water uptake [55]. Attempts to seed abandoned cropland with blue grama have been generally unsuccessful [54]. Lack of adequate soil moisture is probably the major cause of planting failures. The following measures are recommended to minimize planting failures [56]: (1) plant during favorable temperature regimes, (2) control weeds, (3) prepare a firm seedbed so more water will move upward overnight, (4) form shallow basins that will accumulate water, and (5) apply mulch to conserve water. Time of planting is critical for good establishment. Two possible planting strategies are suggested [6]: (1) plant early when temperatures are marginal, but the probability of 2 or more consecutive wet days is relatively high or (2) plant during midsummer when temperatures are favorable, but the probability of 2 or more wet days is low. Blue grama seedlings can be transplanted. Survival of 9-week-old seedlings transplanted onto a Sonoran Desert site averaged 21 percent after 32 months [9]. Transplant mortality may be related to dry soils in spring [9]. Numerous blue grama cultivars have been developed including 'Hachita' and 'Lovington,' both of which originated in New Mexico [23]. 'Lovington' is well adapted for upland sites with medium-textured to fine-textured soils in eastern New Mexico, northwestern Texas, and southeastern Colorado [23]. Recommended planting dates are as follows [49]: Region Planting Dates central Great Plains April to mid-May southern Great Plains April or before Southwest June 15 to July 15 OTHER USES AND VALUES : Blue grama is sometimes used in lawn mixtures [21]. MANAGEMENT CONSIDERATIONS : Blue grama is highly tolerant of livestock grazing and trampling [5] and often increases on heavily grazed sites [51]. This may be due to its ability to maintain a vigorous root system and adequate carbohydrate reserves following defoliation [7]. Some of the leaves grow close to the soil, so some photosynthetic tissue remains after grazing [51]. A greenhouse study showed frequent clipping did not severely reduce blue grama's aboveground production [43]. Another experiment found optimum production occurred when blue grama was clipped at 8-week intervals. At 8-week intervals, aboveground production was maintained and root biomass did not decrease [43]. Average recommended blue grama stubble height at termination of season-long sheep grazing is 0.5 inch (1.3 cm) [35]. Rotation or deferred rotation is advised to maintain production [49]. Blue grama is more resistant to defoliation injury than western wheatgrass (Pascopyrum smithii) [43]. Blue grama may compete with pinyon and juniper seedlings. Like the roots of those seedlings, its are roots concentrated in upper soil layers [27]. Even though a blue grama stand may appear sparse, the surface soil interspaces may be fully occupied by its extensive roots [27]. Tree removal from old-growth pinyon-juniper woodlands generally results in an increase in blue grama. Schott and Pieper [45] noted an average blue grama cover of 1.9 percent in old-growth stands, and 32.9 percent cover in bulldozed stands. Overgrazing may have promoted the spread of junipers [27] beacuse it reduces the number of main roots and root branches of blue grama [8].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Bouteloua gracilis | Blue Grama
GENERAL BOTANICAL CHARACTERISTICS : Blue grama is a warm-season, native perennial [6,46]. This rhizomatous grass typically forms thick, dense sod mats [8]. In the southern portions of its range, however, blue grama is patchy rather than sodlike in growth [47]. Its height varies from 12 to 16 inches (31-41 cm) in the northern parts of its range to 24 to 30 inches (61-76 cm) in southern portions of its range [47]. Plants are leafy at the base [4]; culms reach 7.9 to 23.6 inches (20-60 cm) [46]. Leaves are flat or loosely involute [24]. Blue grama has numerous slender, erect flower stalks with two to five spikes each [51]. Relatively little is known about longevity of blue grama. In a Nebraska study, a majority of plants had died by the end of the third growing season [52]. Percent survival was [52]: Year 1 Year 2 Year 3 100% 66% 45% Blue grama has an extensive, efficient, widely spreading root system. The adundant roots grow from short rhizomes [8]. Fine, fibrous roots are mostly concentrated near the soil surface, although some extend deeper. The majority of roots occur in the upper 13.8 to 29.5 inches (35-75 cm) of the soil, with a few coarser roots extending to depths of 5 to 6 feet (1.5-1.8 m) [8,27]. In Saskatchewan 93 percent of the underground parts of blue grama occurred in the upper 11.8 inches (30 cm) of soil; 84 percent occurred in the upper 5.9 inches (15 cm) [8]. Root depth is generally greater on less xeric sites [8]. RAUNKIAER LIFE FORM : Hemicryptophyte Geophyte REGENERATION PROCESSES : Blue grama regenerates through rhizomes, seed, and tillers [8,51]. In favorable years blue grama produces light seeds which germinate well in warm, moist soil [6]. Seed is dispersed by wind, water, and animals [50]. Rather specific temperature and moisture regimes are necessary for germination. Blue grama requires adequate surface soil moisture for a 2- to 4-day period for germination and initial seminal root growth [55]. It lacks lateral seminal roots, and seedlings die when the surface soil dries out before the seminal root elongates to deeper soil levels [54]. Rainy periods are often too short to permit germination, or surface soils dry out too quickly for establishment [49]. Dung beetles bury blue grama seeds, which may facilitate germination. In a Colorado study, germination was 20 percent for dung beetle-buried seed, and 17 percent for control seed. Seedlings have emerged from aged (6-30 months), partially decomposed cattle dung in the Central Great Plains [54]. Three critical factors for successful growth of blue grama seedlings are (1) initiation of the seminal root, (2) moist soil until at least 6 weeks after emergence, and (3) initiation of adventitious roots [55]. A second wet period of 2 to 4 days is required 2 to 8 weeks after germination for the development of adventitious roots [19,55], which the plant needs to survive the winter [54]. Temperature is also important. Development is most rapid at 68 to 77 degrees Fahrenheit (20-25 deg C) [20]. An average soil temperature above 59 degrees (15 deg C) is necessary for good seedling establishment. A soil water potential of approximately -0.03 megaPascals in the 0- to 16-inch (0-40 cm) zone is required during emergence [55]. Blue grama has developed numerous adaptations for seedling growth and survival in extremely dry environments. Seedlings can increase water uptake, adjust leaf area, and reduce transpiration to avoid drought [56]. SITE CHARACTERISTICS : Blue grama is widely distributed on dry, open grass or sagebrush plains, ridges, foothills, and uplands throughout the West and the Great Plains [4,10]. It occurs in pinyon-juniper and ponderosa pine woodlands to middle elevations in the mountains and on well-vegetated floodplains, washes, and benches [5,10]. Blue grama is also found on waste ground and overgrazed pasturelands [8,21]. Blue grama grows well on sandy loam, sandy, or gravelly soils [10]. In southeastern Arizona, it is most abundant on acidic, relatively infertile sandy and clay-loam soils [37]. Soils are generally low in available nitrate and/or phosphate [37]. Blue grama is well adapted to growth in soils in which water percolates slowly [47]. Blue grama grows within the following elevational ranges [5,13]: from 4,000 to 8,000 feet (1,220-2,440 m) in AZ 3,500 to 10,500 feet (1,068-3,203 m) in CO 2,400 to 5,600 feet (732-1,628l m) in MT 3,200 to 9,500 feet (976-2,898 m) in UT 3,100 to 8,500 feet (946-2,593 m) in WY SUCCESSIONAL STATUS : Obligate Climax Species Blue grama is a climax dominant in shortgrass prairie [6]. It intolerant of heavy shade [53]. SEASONAL DEVELOPMENT : Blue grama begins growing in May or June with the onset of summer rains [46,47]. Growth is rapid under favorable conditions; plants mature in 60 to 70 days [47]. They generally reach 4 to 5 inches (18-28 cm) by midsummer [50]. Growth is largely dependent on the amount of moisture available before the beginning of hot summer weather [47]. In the central Great Plains, blue grama produces flowers and seed within 60 days of the onset of new growth [49]. During drought periods blue grama is dormant, but greens up quickly after moisture is received [10,47]. With sufficient fall precipitation, it produces new growth, sometimes flowering a second [41,51] or, more rarely, a third time [49]. Flowering times are as follows [14,21]: Location Beginning of Flowering End of Flowering CO July September MT July August ND July August WY July September Great Plains June August

FIRE ECOLOGY

SPECIES: Bouteloua gracilis | Blue Grama
FIRE ECOLOGY OR ADAPTATIONS : Blue grama is generally dormant during early spring and in the hottest, driest part of summer. It is also dormant in cold winter months. When warm-season grasses such as blue grama are burned while dormant, living plant parts are often unaffected [53]. Reestablishment occurs through rhizomes, which may be unaffected or even stimulated by fire, and by germination of wind-dispersed, water-dispersed, or animal-dispersed seed [50]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Initial-offsite colonizer (off-site, initial community) Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Bouteloua gracilis | Blue Grama
IMMEDIATE FIRE EFFECT ON PLANT : Fire generally top-kills blue grama. Rhizomes are usually unharmed. This species is generally is less damaged when burned during the spring than when burned during the summer or fall [11,53]. During the spring when soils are moist, heat penetration into the soil is slight, and damage to underground parts is minimal [53]. Blue grama is usually unharmed by fires in years with above normal winter and spring precipitation [58]. It can be severely damaged by fires that occur during drought years [53,58]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : An Arizona study indicated that lethal temperatures of culm bases of sensitive perennial grasses such as blue grama closely approximated existing air temperatures at or near ground level during the hot, dry months of summer. During cooler, moister periods, the lethal temperatures of culm bases were much higher. Over 2 years, the lethal temperature for blue grama growing in pinyon-juniper woodland ranged from 108 to 128 degrees Fahrenheit (60.0-71.2 deg C) [25]. PLANT RESPONSE TO FIRE : Blue grama response to fire varies. It may be harmed, largely unaffected, or increased by fire. Its response depends on season of burning, soil moisture, temperature, plant community composition, and five severity. Recovery is more rapid during years of above average precipitation. Recovery time ranges from 1 to 4 years or more depending on conditions [53,58]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : A Texas study compared postfire blue grama yields after fires carried out in dry and wet years (winter-spring precipitation 0 to 40 percent above normal). Blue grama was tolerant of fire during wet years; there was no loss in herbage yield by the end of the first growing season. Results were as follows [58]: Burned-lb/ha (kg/acre) Unburned-lb/ha (kg/acre) Current Growth Litter Current Growth Litter ----------------------------------------------------------------------------- Wet 1st Yr- 1,680 (1,888) --- --- 1,429 (1,606) 2,474 (2,780) Yrs. 2nd Yr- 1,369 (1,530) 699 (784) 1,247 (1,401) 2,584 (2.904) 3rd Yr- 2,142 (2,407) 1,750 (1,966) 1,754 (1,971) 1,932 (2,171) Dry 1st Yr- 1,100 (1,236) --- --- 3,150 (3,539) 500 (562) yrs. 2nd Yr- 1,840 (2,067) 250 (281) 3,000 (3,371) 500 (562) 3rd Yr- 2,600 (2,921) 330 (371) 2,650 (2,978) 500 (618) When a Central Great Plains blue grama-buffalo grass prairie was burned during the spring of a dry year, yields recovered to 35, 62, and 97 percent at the end of the first, second, and third postfire growing seasons [58]. In a New Mexico study, blue grama herbage was reduced by 30 percent the first year after an early spring fire, but with adequate moisture recovered completely by the second year [15]. At the end of the first growing season after an October fire in Nebraska, productivity of blue grama on burned plots was less than on adjacent control plots [34]: Blue Grama - Phytomass (g/sq m) June July August October Burned Area 21.2 21.5 23.1 12.1 Unburned Control 16.0 22.4 30.3 24.0 However, in Montana, White and Currie [53,59] found that spring burning reduced blue grama yield early in the growing season, but increased productivity later in the same season. The following examples illustrate the variability in response of blue grama to fire: Location Recovery Time/Response Reference Shortgrass prairie 3 years Launchbaugh 1964 harmed by fire in drought Wright & Bailey 1980 yrs.; tolerant when spring- winter precipitation is greater then normal Mixed-grass prairie increased or unaffected Schacht & by spring burning Stubbendieck 1985 Wright & Bailey 1980 Mesic mixed prairie reduced or increased Wright & Bailey 1980 Tallgrass prairie increased after early Wright & Bailey 1980 spring or winter fire Blue Grama Steppe (ND) 4+ years Daubenmire 1968 Canadian Great Plains 3 years Daubenmire 1968 Wright & Bailey 1980 reduced by spring fire Daubenmire 1968 Central Great Plains 2-3 years Wright & Bailey 1980 harmed by fire in dry years Chihuahuan Desert 3 years Ahlstrand 1982 Chihuahuan Desert increased or recovered Ahlstrand 1982 mountain shrub 3 growing seasons after fire New Mexico 2 years Dwyer & Pieper 1967 FIRE MANAGEMENT CONSIDERATIONS : Application of fertilizers such as ammonium sulfate significantly influences yields of blue grama on burned and unburned plots. In New Mexico, plots burned but not fertilized produced 9.0, 11.3, 15.6, and 56.3 percent more blue grama during October, January, June, and April, respectively, than did control plots [14]. Plots burned and fertilized produced 103, 116.9, 164.4, and 173.6 percent more forage in October, January, June, and April than did the control. Plots fertilized in June and left unburned produced 200.1 percent more blue grama than the control [14]. The nutrient content of blue grama is altered by fire. June crude protein levels following a low-intensity April fire in New Mexico were 16.1 percent compared with 14.8 percent on unburned control plots [15]. In a Nebraska study, several species of grasshoppers showed a marked preference for blue grama from burned areas, suggesting potentially higher nutritional value of grama on burned sites [34]. A 3- to 4-month rest from grazing is recommended after fire [57]. Burning blue grama during drought years should be avoided if productivity is to be maintained [59].

REFERENCES

SPECIES: Bouteloua gracilis | Blue Grama
REFERENCES : 1. Ahlstrand, Gary M. 1982. Response of Chihuahuan Desert mountain shrub vegetation to burning. Journal of Range Management. 35(1): 62-65. [296] 2. 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] 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. Blaisdell, James P.; Holmgren, Ralph C. 1984. Managing Intermountain rangelands--salt-desert shrub ranges. Gen. Tech. Rep. INT-163. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 52 p. [464] 5. Bock, Jane H.; Bock, Carl E. 1986. Habitat relationships of some native perennial grasses in southeastern Arizona. Desert Plants. 8(1): 3-14. [478] 6. Briske, D. D.; Wilson, A. M. 1977. Temperature effects on adventitious root development in blue grama seedlings. Journal of Range Management. 30(4): 276-280. [513] 7. Buwai, M.; Trlica, M. J. 1977. Defoliation effects on root weights and total nonstructural carbohydrates of blue grama and western wheatgrass. Crop Science. 17: 15-17. [575] 8. Coupland, Robert T.; Johnson, R. E. 1965. Rooting characteristics of native grassland species of Saskatchewan. Journal of Ecology. 53: 475-507. [702] 9. Cox, Jerry R.; Madrigal, Reynaldo D.; Frasier, Gary W. 1987. Survival of perennial grass transplants in the Sonoran Desert of the Southwestern U.S.A. Arid Soil Research and Rehabilitation. 1: 77-87. [705] 10. 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] 11. Daubenmire, R. 1968. Soil moisture in relation to vegetation distribution in the mountains of northern Idaho. Ecology. 49(3): 431-438. [12942] 12. DeVelice, Robert L.; Ludwig, John A.; Moir, William H.; Ronco, Frank, Jr. 1986. A classification of forest habitat types of northern New Mexico and southern Colorado. Gen. Tech. Rep. RM-131. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 59 p. [781] 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] 14. Dwyer, Don D. 1971. Nitrogen fertilization of blue grama range. Bulletin 585. Las Cruces, NM: New Mexico State University, Agricultural Experiment Station. 8 p. [3521] 15. Dwyer, Don D.; Pieper, Rex D. 1967. Fire effects on blue grama--pinyon-juniper rangeland in New Mexico. Journal of Range Management. 20: 359-362. [833] 16. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 17. Francis, Richard E. 1986. Phyto-edaphic communities of the Upper Rio Puerco Watershed, New Mexico. Res. Pap. RM-272. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 73 p. [954] 18. Francis, Richard E.; Aldon, Earl F. 1983. Preliminary habitat types of a semiarid grassland. In: Moir, W. H.; Hendzel, Leonard, tech. coords. Proceedings of the workshop on Southwestern habitat types; 1983 April 6-8; Albuquerque, NM. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region: 62-66. [956] 19. Frasier, G. W.; Cox, J. R.; Woolhiser, D. A. 1987. Wet-dry cycle effects on warm-season grass seedling establishment. Journal of Range Management. 40(1): 2-6. [964] 20. Fulbright, Timothy E.; Wilson, A. M.; Redente, Edward F. 1985. Green needlegrass and blue grama seedling growth in controlled environments. Journal of Range Management. 38(5): 410-414. [982] 21. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 22. Hanks, Jess P.; Fitzhugh, E. Lee; Hanks, Sharon R. 1983. A habitat type classification system for ponderosa pine forests of northern Arizona. Gen. Tech Rep. RM-97. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 22 p. [1072] 23. Hassell, Wendell G.; Oaks, Wendall R. 1987. Herbaceous plant materials for pinyon-juniper renovation projects. In: Everett, Richard L., comp. Proceedings--pinyon-juniper conference; 1986 January 13-16; Reno, NV. Gen. Tech. Rep. INT-215. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 335-342. [1106] 24. Hitchcock, A. S. 1951. Manual of the grasses of the United States. Misc. Publ. No. 200. Washington, DC: U.S. Department of Agriculture, Agricultural Research Administration. 1051 p. [2nd edition revised by Agnes Chase in two volumes. New York: Dover Publications, Inc.]. [1165] 25. Jameson, Donald A. 1961. Heat and dessication resistance of tissue of important trees and grasses of the pinyon-juniper type. Botanical Gazette. 122: 174-179. [1246] 26. Jameson, Donald A. 1970. Juniper root competition reduces basal area of blue grama. Journal of Range Management. 23(3): 217-218. [1253] 27. Johnsen, Thomas N., Jr. 1962. One-seeded juniper invasion of northern Arizona grasslands. Ecological Monographs. 32(3): 187-207. [1267] 28. Johnston, Barry C. 1987. Plant associations of Region Two: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas. 4th ed. R2-ECOL-87-2. Lakewood, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Region. 429 p. [3519] 29. Kennedy, Kathryn L. 1983. A habitat type classification of the pinyon-juniper woodlands of the Lincoln National Forest, New Mexico. In: Moir, W. H.; Hendzel, Leonard, tech. coords. Proceedings of the workshop on Southwestern habitat types; 1983 April 6-8; Albuquerque, NM. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region: 54-61. [1332] 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. Launchbaugh, J. L. 1964. Effects of early spring burning on yields of native vegetation. Journal of Range Management. 17: 5-6. [1418] 32. Lyon, L. Jack; Stickney, Peter F. 1976. Early vegetal succession following large northern Rocky Mountain wildfires. 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Related categories for Species: Bouteloua gracilis | Blue Grama

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