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Introductory

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
ABBREVIATION : CALCAN SYNONYMS : NO-ENTRY SCS PLANT CODE : CACA4 COMMON NAMES : bluejoint reedgrass bluejoint meadow pinegrass Canadian reedgrass marsh pinegrass marsh reedgrass TAXONOMY : The currently accepted scientific name for bluejoint reedgrass is Calamagrostis canadensis (Michx.) Beauv. This is an exceedingly variable species with one subspecies and eleven varieties described. Recognized subspecies and varieties are as follows [1,12,21,23,39]: C. c. ssp. langsdorffi (Link) Hult. C. c. var. canadensis (Michx.) Beauv. C. c. var. robusta Vasey C. c. var. acuminata Vasey C. c. var. pallida (Vasey & Scriber) Stebbins C. c. var. macouniana (Vasey) Stebbins C. c. var. typicana Stebbins C. c. var. imberbis (Stebbins) C.Hitchc. C. c. var. lactea (W.J. Beal.) C.Hitchc. C. c. var. langsdorfii (Link) Inman C. c. var. scabra (J.Presl.) A.Hitchc. C. c. var. arcta Stebbins. LIFE FORM : Graminoid FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Juile L. Tesky, March 1992. LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Tesky, Julie L. 1992. Calamagrostis canadensis. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
GENERAL DISTRIBUTION : Bluejoint reedgrass is the most common and widespread Calamagrostis species in North America [38]. It occurs throughout the boreal and temperate regions. Bluejoint reedgrass is common in the subarctic from Alaska to Quebec, and extends south to all but the southeastern United States [16,17,38]. ECOSYSTEMS : FRES11 Spruce - fir FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir - spruce FRES25 Larch FRES26 Lodgepole pine FRES28 Western hardwoods FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES36 Mountain grasslands FRES37 Mountain meadows FRES38 Plains grasslands FRES39 Prairie FRES41 Wet grasslands FRES44 Alpine STATES : AK AZ CA CO CT DE HI ID IL IN IA KS KY ME MD MA MI MN MO MT NE NV NH NJ NM NY NC ND OH OR PA RI SD TN UT VA VT WA WV WI WY AB BC LB MB NB NF NT NS ON PE PQ SK YT ADMINISTRATIVE UNITS : ACAD APIS BIHO CACO CRLA CUVA DEWA DENA EFMO FLFO GLBA GLAC GRCA GRTE GRKO INDU ISRO LACL LAVO MORA NOCA PIRO PIPE ROMO SHEN SLBE THRO TICA VOYA WRST YELL YOSE YUCH BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 3 Southern Pacific Border 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 7 Lower Basin and Range 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K005 Mixed conifer forest K007 Red fir forest K008 Lodgepole pine - subalpine forest K010 Ponderosa shrub - forest K011 Western ponderosa pine K012 Douglas-fir forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K021 Southwestern spruce - fir forest K023 Juniper - pinyon woodland K030 California oakwoods K033 Chaparral K034 Montane chaparral K037 Mountain mahogany - oak scrub K038 Great Basin sagebrush K049 Tules marshes K052 Alpine meadows and barren K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlestem K068 Wheatgrass - grama - buffalograss K069 Bluestem - grama prairie K074 Bluestem prairie K081 Oak savanna K093 Great Lakes spruce - fir forest K094 Conifer bog K096 Northeastern spruce - fir forest K098 Northern floodplain forest K104 Appalacian oak forest K111 Oak - hickory - pine forest SAF COVER TYPES : 12 Black spruce 13 Black spruce - tamarack 16 Aspen 18 Paper birch 21 Eastern white pine 22 White pine - hemlock 37 Paper birch - red spruce - balsam fir 38 Tamarack 68 Mesquite 107 White spruce 201 White spruce 202 White spruce - paper birch 204 Black spruce 206 Engelmann spruce - subalpine fir 208 Whitebark pine 212 Western Larch 215 Western white pine 217 Aspen 218 Lodgepole pine 243 Sierra Nevada mixed conifer 246 California black oak 250 Blue oak - Digger pine 251 White spruce - aspen 252 Paper birch 253 Black spruce - white spruce 254 Black spruce - paper birch 255 California coast live oak 256 California mixed subalpine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Bluejoint reedgrass occurs as an understory dominant or codominant in many early seral to climax riparian and cool, moist forest communities. Published classifications listing bluejoint reedgrass as a dominant or codominant in habitat types (hts), dominance types (dts), community types (cts), riparian site types (rst), and plant associations (pas) are listed below: Area Classification Authority AK general veg. pas Viereck & Dyress 1980 AK: interior postfire forest cts Foote 1983 nw AK forest veg. cts Hanson 1953 CO forest hts Arno & Presby 1977 CO hts Powell 1988 w CO riparian veg. cts Baker 1989a nw CO general veg. pas Baker & Kennedy 1985 CO: Arapaho & forest hts Hess & Alexander 1986 Roosevelt NF CO: Gunnison & forest hts Komarkova & others 1988 Uncompahgre NF c ID riparian cts, hts Tuhy & Jensen 1982 n ID forest cts, hts Cooper & others 1991 e ID, w WY forest hts Steele & others 1983 e ID, w WY riparian cts Youngblood & others 1985 MT riparian dts. Hansen & others 1988 MT forest hts Pfister & others 1977 c,e MT riparian veg. rst., cts, hts Hansen & others 1989 nw MT riparian cts Boggs & others 1990 sw MT riparian veg. rst, cts, hts Hansen & others 1989 wc MT wetland cts Pierce & Johnson 1986 UT: Uinta Mt. forest hts Henderson & other 1977 n UT forest hts Mauk & Henderson 1984 UT, se ID riparian cts Padgett & others 1989 WY riparian veg. rst Olson & Gerhart 1982 WY: c YELL riparian hts Mattson 1984 PQ: Saint general veg. pas Darsereau 1957 Lawrence Valley Yukon veg. types Stanek & others 1981

VALUE AND USE

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Bluejoint reedgrass furnishes a large amount of forage for many big game species and livestock [16,18,38]. Occasionally it occupies considerable areas to the exclusion of other native grasses [26]. Under such conditions it yields a large amount of quality hay for livestock [26]. This grass is important forage for livestock in Alaska and is an important component in the diet of bison herds in the Slave River lowland, Northwest Territories, Canada [20]. It is grazed lightly by deer but makes up a major part of the diet of elk in the winter [25,42]. PALATABILITY : Bluejoint reedgrass is most palatable when young and succulent. Since it often grows in wet habitats, use by livestock is often limited until late in the season when the grass is tough [18,38]. The relish and degree of use shown by wildlife species for bluejoint reedgrass in several western states has been rated as follows [8]: MT ND UT WY Pronghorn ---- Poor Poor ---- Elk Fair ---- Fair ---- Mule deer Poor Poor Fair ---- White-tailed deer Poor Poor ---- ---- Small mammals ---- ---- Fair Fair Small nongame birds ---- ---- Fair Fair Upland game birds ---- ---- Poor Poor Waterfowl ---- Fair Poor Fair NUTRITIONAL VALUE : Bluejoint reedgrass has been rated as fair in energy value and poor in protein value [8,15]. In July of 1974, nutrient and mineral composition of this grass on Alaska's Kenai Peninsula were as follows [29]: IVDMD(%)* Fiber % Protein % Moose Dairy Cow Cell walls ADF* Lignin 48.1 55.9 69.8 37.8 3.7 9.8 * IVDMD=in vitro dry-matter digestibility * ADF=acid detergent fiber macronutrients (ppm) micronutrients (ppm) Ca K Mg Na Cu Fe Mn Zn 617.0 9799.0 1481.0 74.0 22.3 58.0 30.9 21.6 COVER VALUE : The degree to which bluejoint reedgrass provides environmental protection during one or more seasons for wildlife species has been rated as follows [8]: MT ND UT WY Pronghorn ---- ---- Poor Poor Elk ---- ---- Poor ---- Mule deer ---- Fair Poor ---- White-tailed deer ---- Good ---- ---- Small mammals Poor ---- Fair Fair Small nongame birds Poor ---- Fair Good Upland game birds Poor ---- Fair Fair Waterfowl Good Fair Fair Fair VALUE FOR REHABILITATION OF DISTURBED SITES : The rhizomatous nature of bluejoint reedgrass helps provide streambank stability. This is particularly important on higher gradient streams where scouring by seasonal flooding is possible [4]. This grass is a vigorous invader of oil spill sites in the Northwest Territories, Canada, and recovers rapidly after spills [16]. Bluejoint reedgrass was evaluated for revegetation in tundra and northern boreal forest sites. It established slowly, but by the end of the growing season, cover and biomass production equaled or exceeded those of commercial varieties. Seed of bluejoint reedgrass has been collected for revegetation trials in Alberta [16]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Grazing: Bluejoint reedgrass is sensitive to overgrazing. Yields decreased by 15 to 20 percent when bluejoint reedgrass was cut two to four times during the growing the season, by 35 to 45 percent when cut five to six times, and about 70 percent when cut seven times, when compared to plots cut once at the end of the growing season [16]. Grazing should be restricted when soils are moist, especially along streams where bank sloughing can occur [13]. Livestock use should be timed according to both the drying of soil surface and the maturation of the seedheads. Livestock should be removed when 40 percent or less utilization of herbaceous forage is obtained [13]. Insect and disease: Some bluejoint strains are susceptible to white top. This condition is caused by insect or fungal damage of the lower culms. Bluejoint, in general, is not susceptible to snow mold [16]. Site competitor: Bluejoint reedgrass is a serious competitor of regeneration of conifer seedlings on disturbed moist sites. Bluejoint reedgrass often produces a thick, "mulch" of litter which insulates the soil surface, causing the soil temperature to decrease. Cold soils could partially explain the poor growth of conifer seedlings that often occurs after planting in bluejoint-reedgrass-dominated sites [19]. Control: Bluejoint reedgrass can be controlled with glyphosate applied after flowering and about the same time as aboveground senescence begins [5].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
GENERAL BOTANICAL CHARACTERISTICS : Bluejoint reedgrass is a sod-forming, native, perennial, cool-season grass [5,12,16,36]. Its blades are numerous and generally obtain a height of 2 to 4 feet (60-120 cm) [12,16]. In Alaska, this grass has been known to reach heights of up to 6.5 feet (200 cm) within 6 weeks [16]. This grass is long-lived. Well-developed fields may persist for as long as 100 years [16]. Creeping underground rhizomes are extensive and fiberous roots are shallow [16,32,36,38]. RAUNKIAER LIFE FORM : Hemicryptophyte Geophyte REGENERATION PROCESSES : Sexual Reproduction: Bluejoint reedgrass flowers are wind pollinated. Prolific flowering, however, occurs only in wetlands and recently disturbed sites [28]. The winged seeds are very lightweight and easily wind-borne [16,28]. Seed yields are low, but seed can remain viable in the soil for up to 5 years [6,16]. Seeds collected near Inuvik, Northwest Territories, had a germination rate of 90 percent at 68 degrees Fahrenheit (20 deg C). Seedling vigor was rated as moderate [3,16]. Vegetative Reproduction: Bluejoint reedgrass can also reproduce vegetatively by rhizomes [6,16,28,33,38]. This grass is capable of producing an extensive network of rhizomes during a single growing season. Small sections (two or more internodes) of several rhizomes can produce shoots and establish new clones [28,33]. SITE CHARACTERISTICS : Bluejoint reedgrass occurs in a wide range of habitats from lowland wet sites, semishaded woodlands, to windswept alpine ridges [16,18]. It extends from sea level in the north and northwest to elevations of over 12,000 feet (3,658 m) near the southern limit of its range in New Mexico [18,38]. It prefers moist sites but can survive in a wide range of moisture regimes [16]. This grass, however, cannot germinate under drought conditions, although it is very drought resistant once established [16]. Soils: Bluejoint reedgrass occupies sites with imperfectly to moderately well-drained soils. It is found on both peat and mineral soils, but most often on peat, and is adapted to a wide range of soil textures. This grass is tolerant of extremely acidic soils, with pH values as low as 3.5, and is moderately tolerant of saline soils [8,16,19]. Plant associates: Bluejoint reedgrass is commonly associated with the following species: Kentucky bluegrass (Poa pratensis), fireweed (Epilobium angustifolium), beaked sedge (Carex rostrata), tufted hairgrass (Deschampsia caespitosa), Geyer willow (Salix geyeriana), booth willow (Salix boothii), wolf's willow (Salix wolfii), subalpine fir (Abies lasiocarpa), lodgepole pine (Pinus contorta), and Engelmann spruce (Picea engelmannii) [13,14,15,30,31,40,41]. SUCCESSIONAL STATUS : Facultative Seral Species Bluejoint reedgrass is a common constituent in a number of seral and climax communities. A combination of sexual and vegetative reproduction allows this grass to persist throughout the successional continuum [4]. It is an aggressive ground residual colonizer and initial off-site colonizer in early seral communities. Once established, a very dense stand of bluejoint reedgrass may persist almost indefinitely, severely limiting the invasion of woody species [5]. In some mid-seral to climax wetland forest communities and forest communities having high water tables, bluejoint reedgrass occurs as a dominant or codominant understory species [13,14,15,31,40]. SEASONAL DEVELOPMENT : In general, bluejoint reedgrass leaf and culm production occurs from early May to mid-June followed by significant vegetative growth of shoot biomass [5,19]. By mid-June flowering heads begin to emerge and by late June to early July flowering begins [5,19]. Flowering peaks from late June to mid-July. Aboveground senescence begins mid to late August [5,19].

FIRE ECOLOGY

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
FIRE ECOLOGY OR ADAPTATIONS : Bluejoint reedgrass sprouts from on-site surviving rhizomes following fire [7,28,35,37]. It can also establish on burned sites by wind-dispersed seeds [7]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Initial-offsite colonizer (off-site, initial community)

FIRE EFFECTS

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
IMMEDIATE FIRE EFFECT ON PLANT : Fire will kill aboveground vegetation of bluejoint reedgrass [35,37]. Severe fires will also kill belowground rhizomes [35,37]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : Under droughty conditions dead shoots of bluejoint reedgrass exhibit low moisture content [20,37]. In small experimental fires in Inuvik, Northwest Territories, dead litter sustained combustion, but the fire merely burned around the live material [37]. PLANT RESPONSE TO FIRE : Following low-severity fires, bluejoint reedgrass will typically sprout from on-site surviving rhizomes. Buried or wind-dispersed seeds may be the primary source of plant establishment on severly burned sites [28,37]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Light surface burning tends to increase the abundance of bluejoint reedgrass [9,35,40]. Following a low-severity burn in a trembling aspen (Populus tremuloides) woodland in southern Ontario, this species' frequency was twice as high on burned areas. The abundance of bluejoint reedgrass 4 months after the fires in 1973 was four times greater than in the control areas and two times greater than in areas burned in 1972 [35]. FIRE MANAGEMENT CONSIDERATIONS : When grazing pressure is light, litter accumulates rapidly [37]. Low-intensity fires can be used to remove this litter and improve forage quality [22]. Because of wet conditions in the spring and summer, successful burning of these communities is limited to the drier fall period [4].

REFERENCES

SPECIES: Calamagrostis canadensis | Bluejoint Reedgrass
REFERENCES : 1. Anderson, J. P. 1959. Flora of Alaska and adjacent parts of Canada. Ames, IA: Iowa State University Press. 543 p. [9928] 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. Bliss, L. C.; Grulke, N. E. 1988. Revegetation in the High Arctic: its role in reclamation of surface disturbance. In: Kershaw, Peter, ed. Northern environmental disturbances. Occas. Publ. No. 24. Edmonton, AB: University of Alberta, Boreal Institute for Northern Studies: 43-55. [14419] 4. Boggs, Keith; Hansen, Paul; Pfister, Robert; Joy, John. 1990. Classification and management of riparian and wetland sites in northwestern Montana. Missoula, MT: University of Montana, School of Forestry, Montana Forest and Conservation Experiment Station, Montana Riparian Association. 217 p. Draft Version 1. [8447] 5. Conn, Jeffery S.; Deck, Richard E. 1991. Bluejoint reedgrass (Calamagrostis canadensis) control with glyphosate and additives. Weed Technology. 5: 521-524. [17408] 6. Conn, Jeffery S.; Farris, Martha L. 1987. Seed viability and dormancy of 17 weed species after 21 months in Alaska. Weed Science. 35: 524-529; 1987. [5] 7. Crane, M. F.; Fischer, William C. 1986. Fire ecology of the forest habitat types of central Idaho. Gen. Tech. Rep. INT-218. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 85 p. [5297] 8. 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] 9. Dyrness, C. T.; Norum, Rodney A. 1983. The effects of experimental fires on black spruce forest floors in interior Alaska. Canadian Journal of Forest Research. 13: 879-893. [7299] 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. 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] 13. Hansen, Paul; Boggs, Keith; Pfister, Robert; Joy, John. 1990. Classification and management of riparian and wetland sites in central and eastern Montana. Missoula, MT: University of Montana, School of Forestry, Montana Forest and Conservation Experiment Station, Montana Riparian Association. 279 p. [12477] 14. Hansen, Paul; Chadde, Steve; Pfister, Robert; [and others]. 1988. Riparian site types, habitat types, and community types of southwestern Montana. Missoula, MT: University of Montana, School of Forestry, Montana Riparian Association. 140 p. [5883] 15. Hansen, Paul; Pfister, Robert; Boggs, Keith; [and others]. 1989. Classification and management of riparian sites in central and eastern Montana. Missoula, MT: University of Montana, School of Forestry, Montana Riparian Association. 368 p. Draft Version 1. [8934] 16. Hardy BBT Limited. 1989. Manual of plant species suitability for reclamation in Alberta. 2d ed. Report No. RRTAC 89-4. Edmonton, AB: Alberta Land Conservation and Reclamation Council. 436 p. [15460] 17. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 18. Herzman, Carl W.; Everson, A. C.; Mickey, Myron H.; [and others]. 1959. Handbook of Colorado native grasses. Bull. 450-A. Fort Collins, CO: Colorado State University, Extension Service. 31 p. [10994] 19. Hogg, Edward H.; Lieffers, Victor J. 1991. The impact of Calamagrostis canadensis on soil thermal regimes after logging in northern Alberta. Canadian Journal of Forest Research. 21: 387-394. [14344] 20. Hogg, E. H.; Lieffers, Victor J. 1991. The relationship between seasonal changes in rhizome carbohydrate reserves and recovery following disturbance in Calamagrostis canadensis. Canadian Journal of Botany. 69: 641-646. [14343] 21. Hulten, Eric. 1968. Flora of Alaska and neighboring territories. Stanford, CA: Stanford University Press. 1008 p. [13403] 22. Kantrud, Harold A.; Millar, John B.; van der Valk, A. G. 1989. Vegetation of wetlands of the prairie pothole region. In: van der Valk, Arnold, ed. Northern prairie wetlands. Ames, IA: Iowa State University Press: 132-187. [15217] 23. Kartesz, John T.; Kartesz, Rosemarie. 1980. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II: The biota of North America. Chapel Hill, NC: The University of North Carolina Press; in confederation with Anne H. Lindsey and C. Richie Bell, North Carolina Botanical Garden. 500 p. [6954] 24. 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] 25. Kufeld, Roland C. 1973. Foods eaten by the Rocky Mountain elk. Journal of Range Management. 26(2): 106-113. [1385] 26. Lamson-Scribner, F. 1900. Economic grasses. Bulletin No. 14. Washington, DC: U.S. Department of Agriculture, Division of Agrostology. 85 p. [4282] 27. 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] 28. MacDonald, S. Ellen; Lieffers, Victor J. 1991. Population variation, outcrossing, and colonization of disturbed areas by Calamagrostis canadensis: evidence from allozyme analysis. American Journal of Botany. 78(8): 1123-1129. [15475] 29. Oldemeyer, J. L.; Franzmann, A. W.; Brundage, A. L.; [and others]. 1977. Browse quality and the Kenai moose population. Journal of Wildlife Management. 41(3): 533-542. [12805] 30. Padgett, Wayne G.; Youngblood, Andrew P.; Winward, Alma H. 1989. Riparian community type classification of Utah and southeastern Idaho. R4-Ecol-89-01. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Region. 191 p. [11360] 31. Pfister, Robert D.; Kovalchik, Bernard L.; Arno, Stephen F.; Presby, Richard C. 1977. Forest habitat types of Montana. Gen. Tech. Rep. INT-34. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 174 p. [1878] 32. Powell, David C. 1988. Aspen community types of the Pike and San Isabel National Forests in south-central Colorado. R2-ECOL-88-01. Denver, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Region. 254 p. [15285] 33. Powelson, R. A.; Lieffers, V. J. 1991. Growth of dormant buds on severed rhizomes of Calamagrostis canadensis. Canadian Journal of Plant Science. 71: 1093-1099. [17592] 34. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 35. Smith, D. W.; James, T. D. W. 1978. Changes in the shrub and herb layers of vegetation after prescribed burning in Populus tremuloides woodland in southern Ontario. Canadian Journal of Botany. 56: 1792-1797. [16400] 36. Stubbendieck, J.; Nichols, James T.; Roberts, Kelly K. 1985. Nebraska range and pasture grasses (including grass-like plants). E.C. 85-170. Lincoln, NE: University of Nebraska, Department of Agriculture, Cooperative Extension Service. 75 p. [2269] 37. Sylvester, T. W.; Wein, Ross W. 1981. Fuel characteristics of arctic plant species and simulated plant community flammability by Rothermel's model. Canadian Journal of Botany. 59: 898-907. [17685] 38. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 39. 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] 40. Viereck, L. A.; Dyrness, C. T.; Batten, A. R.; Wenzlick, K. J. 1992. The Alaska vegetation classification. Gen. Tech. Rep. PNW-GTR-286. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 278 p. [2431] 41. Youngblood, Andrew P.; Padgett, Wayne G.; Winward, Alma H. 1985. Riparian community type classification of eastern Idaho - western Wyoming. R4-Ecol-85-01. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Region. 78 p. [2686] 42. Gullion, Gordon W. 1964. Wildlife uses of Nevada plants. Contributions toward a flora of Nevada No. 49. Beltsville, MD: U. S. Department of Agriculture, Agricultural Research Service, National Arboretum Crops Research Division. 170 p. [6729] 43. 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

Related categories for Species: Calamagrostis canadensis | Bluejoint Reedgrass

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