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Introductory

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
ABBREVIATION : SPHCOC SYNONYMS : Sphaeralcea coccinea (Nutt.) Rydb. [41] SCS PLANT CODE : SPCO SPCOC SPCOE COMMON NAMES : scarlet globemallow red falsemallow common globemallow desert mallow cowboy's delight TAXONOMY : The currently accepted scientific name of scarlet glogemallow is Sphaeralcea coccinea (Pursh.) Rydb. [1,16,23]. Some authorities recognize the following varieties [23]: S. c. var. coccinea S. c. var. dissecta (Nutt.) Kearney S. c. var. elata (Baker) Kearney LIFE FORM : Forb FEDERAL LEGAL STATUS : NO-ENTRY OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : H. Harris, January 1989 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Harris, Holly t. 1989. Sphaeralcea coccinea. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
GENERAL DISTRIBUTION : Scarlet globemallow occurs from the Canadian provinces of British Columbia, Alberta, Saskatchewan, and Manitoba south and eastward to New Mexico, Texas, and Mexico [16,41]. ECOSYSTEMS : FRES15 Oak - hickory FRES17 Elm - ash - cottonwood FRES21 Ponderosa pine FRES28 Western hardwoods FRES29 Sagebrush FRES30 Desert shrub FRES31 Shinnery FRES32 Texas savanna FRES33 Southwestern shrubsteppe FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES37 Mountain meadows FRES38 Plains grasslands FRES39 Prairie FRES40 Desert grasslands STATES : AZ CO ID IA KS MT NM NE NV ND OK OR SD TX UT WA WY AB BC MB SK MEXICO ADMINISTRATIVE UNITS : AGFO ARCH BADL BICA BLCA BRCA CANY CARE CACA CHCU COLM DETO DINO GLAC GLCA GRKO GRSA GUMO JECA LAMR MEVE ROMO SCBL THRO TICA WICA YELL BLM PHYSIOGRAPHIC REGIONS : 5 Columbia Plateau 6 Upper 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 : K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K023 Juniper - pinyon woodland K024 Juniper steppe woodland K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K040 Saltbrush - greasewood K051 Wheatgrass - bluegrass 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 K068 Wheatgrass - grama - buffalograss K070 Sandsage - bluestem prairie K071 Shinnery K074 Bluestem prairie K075 Nebraska sandhills prairie K076 Blackland prairie K081 Oak savanna K086 Juniper - oak savanna K098 Northern floodplain forest SAF COVER TYPES : 220 Rocky Mountain juniper 236 Bur oak 237 Interior ponderosa pine 238 Western juniper 239 Pinyon - juniper 241 Western live oak SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : In many range studies scarlet globemallow is noted as the most common forb in those areas that it is found; however, a grass species is usually identified as the dominant understory species in related plant community information. Scarlet globemallow has been noted as present but not necessarily dominant in several plant typings: Plant associations of Region Two: potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas [22] Grasslands of the Great Plains [40] Analysis of grassland vegetation in selected key areas in southwestern South Dakota [42]

VALUE AND USE

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Scarlet globemallow is commonly eaten by almost all species of herbivores where it occurs and is an important part of the diets of small mammals, pronghorn, sheep, and cattle [17]. PALATABILITY : Scarlet globemallow palatability is generally thought to be fair to poor, although in the southwestern portions of its range it is an important part of the diets of many animals [17,21,34]. Scarlet globemallow provides excellent forage for deer, pronghorn and cattle, and is a staple in black-tailed prairie dog diets [10,13,34]. The degree of use shown by livestock and wildlife species for scarlet globemallow in several western states is rated as follows [7]: Colorado Montana N.Dakota Utah Wyoming -------- ------- -------- ---- ------- Cattle fair fair fair fair fair Sheep fair fair fair fair fair Horses poor poor fair poor fair Pronghorn ---- fair ---- fair good Elk ---- poor ---- fair poor Mule deer ---- poor ---- fair ---- White-tailed deer ---- ---- ---- ---- fair Small mammmals ---- ---- ---- fair ---- Small nongame birds ---- ---- ---- fair ---- Upland game birds ---- ---- ---- fair ---- Waterfowl ---- ---- ---- poor ---- Mule deer diets in New Mexico contained 3 percent scarlet globemallow in a pinyon-juniper/oak area [26], and a study in Colorado determined that scarlet globemallow is the largest single pronghorn dietary item in the summer (18% of total diet) [10]. Summer use and preference values of scarlet globemallow for cattle can be broken down by state: State % of diet Preference Reference ----- --------- ---------- --------- CO 11 --- [18] 15 high [44] SD highest of any forb low [43] NM 25 high [19] Scarlet globemallow was found in higher proportions in cattle diets where it grew on fertilized land in New Mexico [19]. Several studies have examined the importance of scarlet globemallow to black-tailed prairie dogs and other small mammals. Black-tailed prairie dogs apparently prefer scarlet globemallow in fall (September-November) [13,18,35]. The following table presents the percent composition of scarlet globemallow in the diets of several species. Species State Overall Apr/May Jun/Aug Sept/Nov Dec/Mar Reference ------- ----- ------- ------- ------- -------- ------- --------- gopher CO 10 -- 27 -- 1 [38] prairie dog SD -- -- 2 20 -- [13] CO 7 1 5 15 6 [21] cottontail CO 15 5 12 28 14 [21] cattle CO 6 7 11 3 2 [21] NUTRITIONAL VALUE : Scarlet globemallow contains high amounts of vitamin A, low amounts of magnesium and calcium, and is considered highly digestible [17]. Scarlet globemallow roots have a higher seasonal (fall) concentration of carbohydrate reserves than any other organ; the average yearly carbohydrate content in scarlet globemallow is 107 mg per gram of plant [27]. COVER VALUE : Scarlet globemallow provides fair cover for small nongame mammals and birds [7]. VALUE FOR REHABILITATION OF DISTURBED SITES : Scarlet globemallow readily invades disturbed areas. Webb and Guthery [45] found that the percentage of scarlet globemallow cover increased when a northwest Texas mesquite rangeland was disked: 1978 1979 1980 ---- ---- ---- undisked 0.2 0.6 1.9 disked 1.0 0.8 2.3 A similar response occurred after a fire in western North Dakota. These increases are primarily due to a reduction in competition from other plants. The deep rhizomes of scarlet globemallow enable it to survive disking, fires, and grazing; when other species are eliminated scarlet globemallow proliferates [8]. To illustrate the degree to which scarlet globemallow can withstand disturbance, changes in cover percentages following various degrees of soil scarification are presented below [3]: Treatment Year of succession (% cover) --------- first fourth fifth sixth ----- ----- ----- ----- All plants removed with minimal 26 28 22 22 topsoil disturbance Top 30 cm of soil removed 12 18 33 10 Top 1 m of soil removed 1 2 4 4 Top 2 m of soil removed 1 2 4 3 Scarlet globemallow has been known to volunteer on mine spoils to a certain degree [28,32], but is not considered a colonizer on such [39]. Bjugstad and Whitman [4] seeded coal mine spoils in North Dakota, and obtained a maximum of 21 scarlet globemallow plants in a square meter plot, but usually fewer. On bentonite (clay) mine spoils in Montana, scarlet globemallow was the most common forb in the surrounding area, but it did not invade the spoils to any degree [32]. The planting of scarlet globemallow for rehabilitative purposes may not be feasible since the seeds are hard to collect and therefore expensive, and the germination rate is low. Since scarlet globemallow is somewhat palatable and nutritious to livestock, disking or burning the range may increase the occurrence of this plant [30]. OTHER USES AND VALUES : Native North Americans chewed scarlet globemallow and applied it as a paste to relieve the pain of burns and flesh wounds [43]. MANAGEMENT CONSIDERATIONS : Nitrogen fertilization may increase the palatability of scarlet globemallow [19], however fertilization does not increase biomass production [9]. An exception to this is a study done by Goetz [15] in which basal cover of scarlet globemallow increased after fertilization on one site of three; Goetz believes that fertilization results are site specific. In a study of scarlet globemallow invasion patterns, Grygiel, Bonham and Redente [17] found that scarlet globemallow will invade readily where a native grass seed mixture has been planted on disturbed sites, but not where introduced grasses are planted; fertilization made no difference. Disking, burning, and even grazing increases scarlet globemallow production on the range for several years if competition from grasses is limited [8,17]. Scarlet globemallow is also very drought tolerant [21].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
GENERAL BOTANICAL CHARACTERISTICS : Scarlet globemallow is a native, warm-season, perennial forb with a stout woody taproot [34]. Erect or decumbent, this plant is 3 to 12 inches in height (7-30 cm). Leaves are grayish-green and palmately lobed; the light pink to brick red flowers are clustered in terminal spike-like racemes [17]. The roots of scarlet globemallow growing in Saskatchewan have been described by Coupland and Johnson [5]. Maximum root depth is 40 to 72 inches (1-1.8 cm). The tap root decreases in diameter from 0.2 inch (2-5 mm) near the soil surface, to 0.04 inch (1 mm) at the deepest levels. There is little or no branching from the taproot in the top 40 inches (1 m) of soil in the central U.S., however in this study one or two large branches (1-3 mm) are given off 11.8 inches from the surface (30 cm), each as long as 48 inches (1.2 m). These branches follow oblique courses before turning down to parallel the main root. Smaller laterals come off throughout the length of the taproot; secondary branches are scarce. Scarlet globemallow is found in dry areas and is very drought and grazing tolerant; it loses its leaves during times of drought [21] and may actually increase in size in times of drought and overgrazing [17]. Scarlet globemallow will produce seed prolifically only when moisture is available; poor seed germination occurs due to a hard seed coat [17]. Scarlet globemallow reproduces mainly vegetatively by rhizomes [7,17]. RAUNKIAER LIFE FORM : Chamaephyte REGENERATION PROCESSES : Scarlet globemallow has a tendency to reproduce by rhizomes [17] and is a natural colonizer of disturbed sites [17,39]. While it is debatable whether scarlet globemallow will invade mine spoils [4,28,39], it does increase in abundance when the range is disced or burned, perhaps due to a reduction in competition from other plants [8,17,39]. Scarlet globemallow is suppressed as disturbed communities mature, although it is not eliminated [17]. Prolific seed production can occur if moisture is available, however a hard seed coat prevents prolific seed germination [17]. Roth, Holechek, and Hussain [30] applied mechanical and chemical treatments to scarlet globemallow seeds to determine if germination might improve. Seed scarification by soaking in sulfuric acid allowed a higher than normal germination rate, as did soaking in dioxane, an organic material. Mechanical treatments (i.e., carpel removal and scarification of seed coat) improved germination, but embryos died withing one week. Since dioxane is carcinogenic and highly flammable, sulfuric acid is recommended to potentially increase the germination rate of native globemallow species. Applications of fertilizers seem to have little effect on scarlet globemallow production [9], except in certain local range conditions [15]. However, fertilizing globemallow may improve rangeland by reducing the exploitation of other plants by livestock [19]. SITE CHARACTERISTICS : Scarlet globemallow grows mainly in dry grassland prairies at elevations of 3,500 to 9,000 feet (1,067-2,473 m) [7]. Precipitation in the central and northwestern grassland areas averages 10 to 40 inches (26-100 cm) falling mostly in summer; temperatures vary from -20 degrees Fahrenheit in winter to 85 degrees Fahrenheit in summer (-29 - 32 degrees C) [11]. Scarlet globemallow growth in specific soils are rated as follows [7]: UT CO WY MT ND ------ ------ ------ ------ ------ gravel fair poor fair poor fair sand good fair good fair fair sandy loam good good good good good loam good good good good good clay loam good good good good good clay fair fair fair fair fair dense clay poor poor poor poor poor Scarlet globemallow was most commonly found in sandy loam and loam in a study in Colorado [20]. SUCCESSIONAL STATUS : Scarlet globemallow is considered a pioneer on disturbed sites and is present in early seral stages [31,39]. This species will aggressively invade an open area, but will not aggressively compete with established plants, especially grasses. After infiltrating newly disturbed areas, scarlet globemallow is somewhat suppressed by competing species as the community matures, although it maintains a constant presence in the community; scarlet globemallow will release again if a second disturbance occurs [17]. SEASONAL DEVELOPMENT : Phenologic Event Date Reference ---------------- ---- --------- growth starts March (New Mexico) [24] April-May (Colorado) [7] flowers bloom and fruit matures April-October [7,24] stem elongation May [27] fall quiescence November [27]

FIRE ECOLOGY

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
FIRE ECOLOGY OR ADAPTATIONS : Scarlet globemallow is able to survive fires since the bulk of the plant is situated underground [8]. Rhizomes will send new shoots up soon after fire and other disturbances [17]. Scarlet globemallow is a colonizing species; it invades disturbed areas readily and proliferates until grasses begin to outcompete it [8,17]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil

FIRE EFFECTS

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
IMMEDIATE FIRE EFFECT ON PLANT : The aerial portions of scarlet globemallow are killed by fire, but extensive rhizomes allow it to resprout immediately (same season) following a fire [8]. Scarlet globemallow is thought to increase in abundance and vigor after fire [17]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Dix [8] compared the frequency of scarlet globemallow on a burned North Dakota grassland site and adjacent unburned sites: burned unburned ------ -------- Squaw Creek 42 12 North Rim 12 10 More scarlet globemallow plants existed on the burned sites due to a lack of competition from grasses. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Sphaeralcea coccinea | Scarlet Globemallow
REFERENCES : 1. Bare, Janet E. 1979. Wildflowers and weeds of Kansas. Lawrence, KS: The Regents Press of Kansas. 509 p. [3801] 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. Biondini, Mario E.; Bonham, Charles D.; Redente, Edward F. 1985. Secondary successional patterns in a sagebrush (Artemisia tridentata) community as they relate to disturbance and soil biological activity. Vegetatio. 60: 25-36. [448] 4. Bjugstad, Ardell J.; Whitman, Warren C. 1982. Perennial forbs for wildlife habitat restoration on mined lands in the northern Great Plains. In: Western proceedings, 62nd annual conference of the Western Association of Fish and Wildlife Agencies; 1982 July 19-22; Las Vegas, Nevada. [Place of publication unknown]: [Publisher unknown]: 257-271. On file with: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Lab, Missoula, MT. [2932] 5. Coupland, Robert T.; Johnson, R. E. 1965. Rooting characteristics of native grassland species of Saskatchewan. Journal of Ecology. 53: 475-507. [702] 6. Dickinson, C. E.; Dodd, Jerrold L. 1976. Phenological pattern in the shortgrass prairie. American Midland Naturalist. 96(2): 367-378. [799] 7. 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] 8. Dix, Ralph L. 1960. The effects of burning on the mulch structure and species composition of grasslands in western North Dakota. Ecology. 41(1): 49-56. [808] 9. 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] 10. Ellis, James E.; Travis, Michael. 1975. Comparative aspects of foraging behaviour of pronghorn antelope and cattle. Journal of Applied Ecology. 12(2): 411-420. [4645] 11. Espenshade, Edward B., Jr., editor. 1987. Goode's world atlas. 17 ed. Chicago, IL: Rand McNally. 367 p. [4852] 12. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 13. Fagerstone, K. A.; Tietjen, H. P.; Williams, O. 1981. Seasonal variation in the diet of black-tailed prairie dogs. Journal of Mammalogy. 62(4): 820-824. [906] 14. 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] 15. Goetz, Harold. 1969. Composition and yields of native grassland sites fertilized at different rates of nitrogen. Journal of Range Management. 22(6): 384-390. [1029] 16. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 17. Grygiel, Carolyn E; Bonham, Charles D.; Redente, Edward F. 1984. Combined effects of environmental and agronomic factors on the invasion patterns of Sphaeralcea coccinea (Nutt.) Rydb. (Malvacea). Phytologia. 56(3): 145-153. [4641] 18. Hansen, Richard M.; Gold, Ilyse K. 1977. Blacktail prairie dogs, desert cottontails and cattle trophic relations on shortgrass range. Journal of Range Management. 30(3): 210-214. [4644] 19. Havstad, Kris; Pieper, Rex D.; Donart, Gary B.; {and others]. 1979. Cattle diets on a fertilized blue grama upland range site. Journal of Range Management. 32(5): 398-401. [4646] 20. Hyder, D. N.; Bement, R. E.; Remmenga, E. E.; Terwilliger, C., Jr. 1966. Vegetation-soils and vegetation-grazing relations from frequency data. Journal of Range Management. 19: 11-17. [1234] 21. Johnson, James R.; Nichols, James T. 1970. Plants of South Dakota grasslands: A photographic study. Bull. 566. Brookings, SD: South Dakota State University, Agricultural Experiment Station. 163 p. [18501] 22. 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] 23. Kearney, Thomas H.; Peebles, Robert H.; Howell, John Thomas; McClintock, Elizabeth. 1960. Arizona flora. 2d ed. Berkeley, CA: University of California Press. 1085 p. [6563] 24. Kemp, Paul R. 1983. Phenological patterns of Chihuahuan desert plants in relation to the timing of water availability. Journal of Ecology. 71: 427-436. [5054] 25. 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] 26. Mahgoub, El Fatih; Pieper, Rex D.; Holechek, Jerry L.; [and others]. 1987. Botanical content of mule deer diets in south-central New Mexico. New Mexico Journal of Science. 27(1): 21-27. [3259] 27. Menke, John W.; Trlica, M. J. 1981. Carbohydrate reserve, phenology, and growth cycles of nine Colorado range species. Journal of Range Management. 34(4): 269-277. [1639] 28. Parady, Fred E., III. 1984. Reclamation techniques in southwestern Wyoming. In: Symposium on the reclamation of lands disturbed by surface mining: a cornerstorne for communication and understanding: Proceedings, 1984 annual meeting of the American Society for Surface Mining and Reclamation: 1984 July 10-13; Owensboro, KY. [Place of publication unknown]: [Publisher unknown]: 87-92. [1813] 29. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 30. Roth, Timothy E.; Holechek, J. L.; Hussain, Mohammed Y. 1987. Germination response of three globemallow species to chemical treatment. Journal of Range Management. 40(2): 173-175. [4643] 31. Schott, M. R.; Pieper, R. D. 1987. Succession of pinyon-juniper communities after mechanical disturbance in southcentral New Mexico. Journal of Range Management. 40(1): 88-94. [3913] 32. Sieg, Carolyn Hull; Uresk, Daniel W.; Hansen, Richard M. 1983. Plant-soil relationships on bentonite mine spoils and sagebrush- grassland in the northern High Plains. Journal of Range Management. 36(3): 289-294. [4642] 33. 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] 34. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 35. Summers, Carol A.; Linder, Raymond L. 1978. Food habits of the black-tailed prairie dog in western South Dakota. Journal of Range Management. 31(2): 134-136. [2294] 36. 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] 37. 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] 38. Vaughan, Terry A. 1967. Food habits of the northern pocket gopher. American Midland Naturalist. 77(1): 176-189. [2427] 39. Wagner, Warren L.; Martin, William C.; Aldon, Earl F. 1978. Natural succession on strip-mined lands in northwestern New Mexico. Reclamation Review. 1: 67-73. [2436] 40. Weaver, J. E.; Albertson, F. W. 1956. Grasslands of the Great Plains. Lincoln, NE: Johnsen Publishing Company. 395 p. [2463] 41. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. [2944] 42. Whitman, W. C. 1979. Analysis of grassland vegetation on selected key areas in southwestern North Dakota. A report on a project of the North Dakota regional environmental assessment Program. Contract No. 7-01-2. Fargo, ND: North Dakota State University, Department of Botany. [Total pages unknown]. [3321] 43. Uresk, Daniel W. 1986. Food habits of cattle on mixed-grass prairie on the Northern Great Plain Plains. Prairie Naturalist. 18(4): 211-218. [94] 44. Vavra, M.; Rice, R. W.; Hansen, R. M.; Sims, P. L. 1977. Food habits of cattle on shortgrass range in northeastern Colorado. Journal of Range Management. 30(4): 261-263. [5628] 45. Webb, William M.; Guthery, Fred S. 1983. Response of wildlife food plants to spring discing of mesquite rangeland in northwest Texas. Journal of Range Management. 36(3): 351-353. [4344]

Index

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