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Introductory

SPECIES: Calamagrostis montanensis | Plains Reedgrass
ABBREVIATION : CALMON SYNONYMS : NO-ENTRY SCS PLANT CODE : CAMO COMMON NAMES : plains reedgrass prairie reedgrass TAXONOMY : The currently accepted scientific name for plains reedgrass is Calamagrostis montanensis (Scribn.) Scribn. There are no recognized subspecies, varieties, or forms [14,16,17,18,24]. LIFE FORM : Graminoid FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Julie L. Tesky, April 1992. LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Tesky, Julie L. 1992. Calamagrostis montanensis. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Calamagrostis montanensis | Plains Reedgrass
GENERAL DISTRIBUTION : Plains reedgrass occurs from Manitoba to Alberta, south to Minnesota, North Dakota, South Dakota, Montana, Idaho, Wyoming, and Colorado [13,14,16,17,18]. ECOSYSTEMS : FRES21 Ponderosa pine FRES29 Sagebrush FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES38 Plains grasslands FRES39 Prairie STATES : CO ID MN MT ND SD WY AB BC MB SK ADMINISTRATIVE UNITS : DETO ROMO THRO BLM PHYSIOGRAPHIC REGIONS : 10 Wyoming Basin 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 K038 Great Basin sagebrush K055 Sagebrush steppe K056 Wheatgrass - needlegrass 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 SAF COVER TYPES : 237 Interior ponderosa pine 239 Pinyon - Juniper SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Plains reedgrass occurs as an associate in grazed communities dominated by blue grama (Bouteloua gracilis) [4]. However, it has not been listed in published classification schemes.

VALUE AND USE

SPECIES: Calamagrostis montanensis | Plains Reedgrass
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Plains reedgrass provides forage for sheep, cattle, and horses [24]. It is also consumed by deer, elk, and small mammals [9,25]. PALATABILITY : Plains reedgrass coarse leaves are considered less palatable than most prairie species it occurs with [2]. The relish and degree of use shown by livestock and wildlife species for plains reedgrass in several western states is rated as follows [9,25]: CO MT ND WY Cattle Fair Fair ---- Fair Sheep Fair Fair Fair Fair Horses Fair Fair Fair Fair Elk ---- Fair-Good ---- ---- Deer ---- Poor-Fair ---- ---- NUTRITIONAL VALUE : Plains reedgrass has been rated as fair in energy value and poor in protein value [9]. COVER VALUE : The degree to which plains reedgrass provides environmental protection during one or more seasons for wildlife species is rated as follows [9]: MT ND WY Pronghorn ---- Poor Poor Elk ---- ---- Poor Mule deer ---- Good Poor White-tailed deer ---- Good Poor Small mammals ---- ---- Fair Small nongame birds Fair ---- ---- Upland game birds Fair ---- ---- Waterfowl Poor ---- ---- VALUE FOR REHABILITATION OF DISTURBED SITES : Because plains reedgrass is rhizomatous and exhibits aggressive growth after disturbance, it can be used for erosion control. It also has potential for long-term revegetation of disturbed sites [9]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Grazing: Plains reedgrass increases in response to grazing [4,7]. When comparing grazed and ungrazed sites of a mixed-grass community, Brand and Goetz [4] found that the average herbage production of plains reedgrass on grazed rangeland was 41 times greater than on ungrazed lands. Herbicides: Plains reedgrass increased in range areas after spraying with 2,4-D [6].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Calamagrostis montanensis | Plains Reedgrass
GENERAL BOTANICAL CHARACTERISTICS : Plains reedgrass is a native, cool-season, perennial grass [8,12,22,24]. The culms grow from 6 to 16 inches (15-40 cm) tall [16,17,22,24]. The mostly basal leaves have smooth sheaths and strongly rolled blades [22]. The rhizomes are slender with short paperish leaves at each node. Roots arise from the nodes and are similar to the rhizomes in thickness. Maximum root-depth ranges from 3.28 to 4.92 feet (1-1.5 m) [8]. RAUNKIAER LIFE FORM : Chamaephyte Cryptophyte (Geophyte) REGENERATION PROCESSES : Plains reedgrass regenerates sexually, and vegetatively through rhizomes [23]. Specific information on seed dispersal and viability is lacking. SITE CHARACTERISTICS : Plains reedgrass occurs on plains and dry open areas of grasslands, sagebrush benchlands, and foothills from 4,800 to 8,500 feet (1,463-2,591 m) in elevation [9,16,17,18,21]. It grows in sandy loams, loams, clay loams, and clayey soils [9,19]. Climate: In areas where plains reedgrass commonly occurs, moisture is usually available early in the growing season but later becomes limited. Summers are marked by high temperatures and low humidity creating a dry climate. In winter, snowfall is considerable and temperatures may drop to -20 degrees Fahrenheit (-29 deg C) [27]. Plant associates: Plains reedgrass is commonly associated with the following species: needle-and-thread (Stipa comata), green needlegrass (S. viridula), blue grama, prairie junegrass (Koeleria cristata), bluebunch wheatgrass (Pseudoroegneria spicata), rough fescue (Festuca scrubrella), Idaho fescue (F. idahoensis), and threetip sagebrush (Artemisia tripartita) [3,4,7,25,27]. SUCCESSIONAL STATUS : Facultative Seral Species Plains reedgrass is an early seral to climax species. It increases following disturbance and commonly persists for several years. On some grazed ranges, plains reedgrass maintains subdominance with other shortgrass species [4]. This grass also occurs in mixed prairie climax communities dominated by Agropyron and Stipa spp. [7]. Plains reedgrass abundance on sandy soils is generally an indicator of late seral stages [7]. SEASONAL DEVELOPMENT : Plains reedgrass growth begins in early April followed by the initiation of fruiting stalks in late May [12]. Flowering generally begins in late June to July and ends in August [9,12]. Seeds mature in late July and are shed in mid-August [12].

FIRE ECOLOGY

SPECIES: Calamagrostis montanensis | Plains Reedgrass
FIRE ECOLOGY OR ADAPTATIONS : Plains reedgrass appears to be well adapted to periodic burning. Postburn establishment quickly occurs through sprouting of on-site surviving rhizomes and, presumably, through colonization from off-site seed sources [2,5]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Calamagrostis montanensis | Plains Reedgrass
IMMEDIATE FIRE EFFECT ON PLANT : Although fire will kill aboveground parts of plains reedgrass, underground rhizomes survive even high-severity fires [2]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Even after high-severity fire, plains reedgrass will sprout vigorously from on-site surviving rhizomes. This grass provides more forage on burned sites than on unburned sites [2]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Three years following an August sagebrush-grass fire on the upper Snake River plains, Idaho, plains reedgrass exceeded its original density on burned sites. At postfire year 9 this grass was still producing significantly more herbage on burned sites than on unburned sites [2]. FIRE MANAGEMENT CONSIDERATIONS : Prescribed burning is a valuable management tool for range improvement [2,5,15]. Herbage production of perennial grasses and forbs often increase within a year after burning [2]. Burning favors rhizomatous grasses such as plains reedgrass if plants are burned when dormant [2,5]. Range managers have suggested that grazing be deferred in burned areas for at least 1 year to allow for the uninterrupted growth of herbaceous vegetation [5].

REFERENCES

SPECIES: Calamagrostis montanensis | Plains Reedgrass
REFERENCES : 1. 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] 2. Blaisdell, James P. 1953. Ecological effects of planned burning of sagebrush-grass range on the upper Snake River Plains. Tech. Bull. 1975. Washington, DC: U.S. Department of Agriculture. 39 p. [462] 3. Blaisdell, James P. 1958. Seasonal development and yield of native plants on the upper Snake River Plains and their relation to certain climatic factors. Tech. Bull. 1190. Washington, DC: U.S. Department of Agriculture. 68 p. [463] 4. Brand, M. D.; Goetz, H. 1978. Secondary succession of a mixed grass community in southwestern North Dakota. Annual Proceedings of the North Dakota Academy of Science. 32(2): 67-78. [7512] 5. Britton, Carlton M.; Ralphs, Michael H. 1979. Use of fire as a management tool in sagebrush ecosystems. In: The sagebrush ecosystem: a symposium: Proceedings; 1978 April; Logan, UT. Logan, UT: Utah State University, College of Natural Resources. 101-109. [518] 6. Carr, Harold D. 1967. Effects of sagebrush spraying on abundance, distribution and movements of sage grouse. Fort Collins, CO: Colorado State University. 106 p. Thesis. [5877] 7. Coupland, Robert T. 1961. A reconsideration of grassland classification in the northern Great Plains of North America. Journal of Ecology. 49: 135-167. [12588] 8. Coupland, Robert T.; Johnson, R. E. 1965. Rooting characteristics of native grassland species of Saskatchewan. Journal of Ecology. 53: 475-507. [702] 9. 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] 10. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 11. 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] 12. Goetz, Harold. 1963. Growth and development of native range plants in the mixed grass prairie of western North Dakota. Fargo, ND: North Dakota State University. 141 p. Thesis. [5661] 13. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 14. Hallsten, Gregory P.; Skinner, Quentin D.; Beetle, Alan A. 1987. Grasses of Wyoming. 3rd ed. Research Journal 202. Laramie, WY: University of Wyoming, Agricultural Experiment Station. 432 p. [2906] 15. Higgins, Kenneth F.; Kruse, Arnold D.; Piehl, James L. 1989. Prescribed burning guidelines in the Northern Great Plains. Ext. Circ. EC-760. Brookings, SD: South Dakota State University, Cooperative Extension Service, South Dakota Cooperative Fish and Wildlife Research Unit. 36 p. [14185] 16. 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] 17. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 18. 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] 19. Hubbard, William A. 1950. The climate, soils, and soil-plant relationships of an area in southwestern Saskatchewan. Scientific Agriculture. 30(8): 327-342. [6263] 20. 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] 21. Lackschewitz, Klaus. 1986. Plants of west-central Montana--identification and ecology: annotated checklist. Gen. Tech. Rep. INT-217. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 128 p. [2955] 22. Lackschewitz, Klaus. 1991. Vascular plants of west-central Montana--identification guidebook. Gen. Tech. Rep. INT-227. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 648 p. [13798] 23. Lyon, L. Jack; Stickney, Peter F. 1976. Early vegetal succession following large northern Rocky Mountain wildfires. In: Proceedings, Tall Timbers fire ecology conference and Intermountain Fire Research Council fire and land management symposium; 1974 October 8-10; Missoula, MT. No. 14. Tallahassee, FL: Tall Timbers Research Station: 355-373. [1496] 24. Morris, H. E.; Booth, W. E.; Payne, G. F.; Stitt, R. E. 1950. Important grasses on Montana ranges. Bull. No. 470. Bozeman, MT: Montana Agricultural Experiment Station. 52 p. [5520] 25. 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] 26. Ferguson, Dennis E.; Boyd, Raymond J. 1988. Bracken fern inhibition of conifer regeneration in northern Idaho. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 11 p. [2834] 27. Taylor, John Edgar. 1967. Range pitting and nitrogen fertilization on mixed prairie rangeland in northern Montana. Bozeman, MT: Montana State University. 71 p. Thesis. [12328] 28. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of scientific plant names. Vol. 1. List of plant names. SCS-TP-159. Washington, DC. 416 p. [11573] 29. Vogel, W. G.; Van Dyne, G. M. 1966. Vegetation responses to grazing management on a foothill sheep range. Journal of Range Management. 19: 80-85. [12263] 30. Whitman, Warren C. 1979. Analysis of grassland vegetation on selected key areas in southwestern North Dakota. Final Report on Contract No. 7-01-2. Bismark, ND: Regional Environmental Assessment Program. 199 p. [12529] 31. Zacek, Joseph C.; Hunter, Harold E.; Bown, T. A.; Ross, Robert L. 1977. Montana grazing guides. U.S. Department of Agriculture, Soil Conservation Service. 12 p. [2687] 32. 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]

Index

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