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Introductory

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
ABBREVIATION : STIRIC SYNONYMS : NO-ENTRY SCS PLANT CODE : STRI2 COMMON NAMES : Richardson needlegrass spreading needlegrass TAXONOMY : The currently accepted scientific name for Richardson needlegrass is Achnatherum richardsonii (Link) Barkworth [40]. LIFE FORM : Graminoid FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Lora L. Esser November 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Esser, Lora L. 1992. Achnatherum richardsonii. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
GENERAL DISTRIBUTION : Richardson needlegrass is distributed from British Columbia, Alberta, Saskatchewan, and parts of Yukon Territory [18,36] south through Montana to Colorado and west to eastern Washington [14,18]. Scattered populations occur in the Black Hills of South Dakota [14]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES26 Lodgepole pine FRES29 Sagebrush FRES36 Mountain grasslands FRES37 Mountain meadows FRES38 Plains grasslands STATES : CO ID MT SD WA WY AB BC SK YT ADMINISTRATIVE UNITS : BIHO GLAC GRTE YELL BLM PHYSIOGRAPHIC REGIONS : 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K012 Douglas-fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K024 Juniper steppe woodland K050 Fescue - wheatgrass K051 Wheatgrass - bluegrass K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K066 Wheatgrass - needlegrass SAF COVER TYPES : 201 White spruce 210 Interior Douglas-fir 217 Aspen 218 Lodgepole pine 219 Limber pine 220 Rocky Mountain juniper 237 Interior ponderosa pine 238 Western juniper 251 White spruce - aspen SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Richardson needlegrass is found in intermontane valley grasslands and meadows [24]. It is also common in bottomlands, on rocky or wooded slopes, and on hillsides in mature pine (Pinus spp.) forests [12,14]. In British Columbia, Richardson needlegrass commonly occurs on warm, dry sites scattered througout major valleys of the sub-boreal zone [25]. Published classifications describing Richardson needlegrass as a codominant in community types are listed below: Grasslands of the North Fork Valley, Glacier National Park, Montana [16]. Fescue grasslands of western Canada [19]. Common plant associates of Richardson needlegrass not listed in Distribution and Occurrence are: Canada bluegrass (Poa compressa), prairie junegrass (Koeleria cristata), rough fescue (Festuca scabrella), Idaho fescue (F. idahoensis), bearded wheatgrass (Elymus caninus), western needlegrass (Achnatherum occidentalis), timber danthonia (Danthonia intermedia), tufted hairgrass (Deschampsia cespitosa), sedges (Carex spp.), shrubby cinqefoil (Potentilla fruticosa), bearberry (Arctostaphylos uva-ursi), timothy (Phleum pratense), common yarrow (Achillea millefolium), prairiesmoke avens (Geum triflorum), northern bedstraw (Galium boreale), Hood's phlox (Phlox hoodii), and bluebell (Campanula rotundifolia) [21,23,30,34].

VALUE AND USE

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Richardson needlegrass is an important forage species for livestock on the northern Great Plains [15]. It is also utilized by deer, bighorn sheep, and elk [7]. At lower elevations in western Montana, cattle graze Richardson needlegrass from late spring until early fall. At higher elevations, grazing is limited to the summer months [7]. Needlegrasses (Achnatherum spp.) rank high as forage grasses on the western ranges because of their abundance, wide distribution, long growing period, and capacity to cure well on the ground [32]. At maturity, the long, sharp awns of needlegrasses become dangerous to grazing animals and can cause injuries to the eyes, ears, and skin [32]. Reports of livestock injuries caused by Richardson needlegrass, however, are not documented in the available literature. PALATABILITY : Palatability of Richardson needlegrass varies with phenological development. Palatability is highest in the spring and early summer when plants are young and succulent. Richardson needlegrass is less palatable at maturity, when it becomes coarse and wiry [31]. In Montana, the palatability of Richardson needlegrass is rated as fair for deer, fair to good for elk, and good for sheep and cattle [21]. NUTRITIONAL VALUE : The nutritional value of Richardson needlegrass during five major stages of growth are as follows (values are percentage of dry weight with the exception of carotene which is in mg/kg) [1,15]: Leaf Heading Seed-ripe Cured Weathered Stage Dry Matter 93.0 92.5 93.1 93.3 95.4 Protein 10.3 6.65 5.13 4.10 2.60 Crude Fat 2.55 2.60 2.27 3.00 2.60 Crude Fiber 31.2 31.2 34.7 31.1 38.4 Ash 7.20 6.00 7.40 6.10 4.50 Calcium 0.33 0.30 0.33 0.38 0.36 Phosphorus 0.15 0.08 0.08 0.07 0.04 Cellulose 31.3 34.6 35.8 34.8 40.5 Carotene 33.1 31.5 5.67 3.50 1.15 COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : Fescue (Festuca spp.) grasslands are an important grazing resource in much of the West, and Richardson needlegrass is an important component of these grasslands. Richardson needlegrass decreases with overgrazing [19]. On lightly to moderately disturbed sites, Richardson needlegrass increases. On more severely disturbed sites, Richardson needlegrass decreases. Richardson needlegrass increases on moist disturbed sites [19].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
GENERAL BOTANICAL CHARACTERISTICS : Richardson needlegrass is a native, perennial, cool-season bunchgrass. This fine-stemmed, tufted grass grows from 16 to 40 inches (40-100 cm) tall [10,18]. The inflorescence is open and diffuse [18]. Culms are glabrous or slightly hairy. Blades are typically involute and subfiliform and reach heights of about 6 to 10 inches (15-25 cm) [14]. The seeds of Richardson needlegrass are hard, slender, and cylindrical, and have a sharp, pointed base (callus) and long, twisted awns [31]. Richardson needlegrass is a shallow-rooted species; the abundance of roots decreases as soil depth increases. Clay accumulation restricts root penetration of Richardson needlegrass [22]. Richardson needlegrass becomes dormant following depletion of surface soil moisture during the latter part of the growing season [22]. RAUNKIAER LIFE FORM : Hemicryptophyte REGENERATION PROCESSES : Richardson needlegrass reproduces sexually. The twisted awns of the seeds expand and contract with variations in temperature and moisture, drilling them into the soil [31,36]. Strong winds may transport seeds a considerable distance, especially when awns are twisted together in clumps. Animals also carry seeds as the awns become trapped in their fur [36]. SITE CHARACTERISTICS : Richardson needlegrass is common on hillsides and dry plains, in open grassland or sagebrush benches, and in bottomlands, swales, and wooded slopes [3,10]. It is also found on moraines and gravel outwash associated with streams [3]. In Montana, Richardson needlegrass is found on mountain slopes on both sides of the Continental Divide at elevations of 3,000 to 7,000 feet (900-2,100 m) [21]. In north-central Colorado, it is found in mesic sites at 8,000 to 8,600 feet (2,400-2,580 m) [13]. In Wyoming, Richardson needlegrass is commonly found at elevations of 7,000 to 8,500 feet (2,134-2,591 m) and occasionally at elevations of 9,000 feet (2,743 m) [3]. Soils: Richardson needlegrass is common on slightly acidic to neutral soil (pH 6.6-7.3) [19]. Soil textures vary from fine sandy loam to clayey loam. Cation exchange capacity is moderately high, but soils are considered of low fertility because of low levels of nitrogen and phosphorus [19]. SUCCESSIONAL STATUS : Obligate Climax Species Richardson needlegrass is a climax codominant on sites in Glacier National Park and on fescue grasslands of western Canada [16,19]. It occurs in the rough fescue prairie association, a climax community type. However, the equilibrium between prairie and associated forest vegetation is not always clear. Woody species such as willows (Salix spp.) and poplars (Populus spp.) are tending to invade the fescue prairie of Alberta, though the effects of fire, mowing, and limited grazing may serve to counteract this tendency. It has been suggested that white spruce (Picea glauca) may be considered as the theoretical climax for much of the fescue grassland or black soil region of Alberta; however, natural burning tends to prevent this cimax from being realized [39]. SEASONAL DEVELOPMENT : Most needlegrasses begin vegetative growth in the early spring, usually before associated grasses green up, and continue growing throughout the summer if enough moisture is available [31,32]. Needlegrasses flower from July to September [31]. No specific information on the seasonal development of Richardson needlegrass was found.

FIRE ECOLOGY

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
FIRE ECOLOGY OR ADAPTATIONS : Perennial needlegrasses are among the least fire resistant of the bunchgrasses [35]. No specific information on adaptations of Richardson needlegrass to fire was found. Season of burn and plant size contribute to needlegrasses' ability to survive fire. Needlegrasses tend to be more susceptible to fire when burned during midsummer. Plants with smaller crown diameters more often survive fire than do larger plants. Successive years' accumulation of dead culm and leaves make older needlegrasses highly susceptible to burning. Needlegrasses may often survive low-intensity fires, as heat is not transferred below the soil surface [37]. POSTFIRE REGENERATION STRATEGY : Tussock graminoid

FIRE EFFECTS

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
IMMEDIATE FIRE EFFECT ON PLANT : Specific fire effects probably depend largely on season of burn, phenology, and fire intensity and severity. Generally, needlegrasses (Achnatherum spp.) are top-killed by fire. Occasionally, a few culms may survive along the periphery of the crown. When fire severity is moderate to high, heat may be transferred below the soil surface, damaging roots and killing the plant. Needlegrasses often exhibit subsurface charring following fire [37]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Production of most needlegrasses is initially reduced by fire; the degree of reduction appears dependent on species and season of burn [11]. In southwestern Montana, however, production of Richardson needlegrass in a rough fescue habitat type with a heavy preburn canopy of mountain big sagebrush (Artemisia tridentata var. vaseyana) increased from 4 pounds per acre (1.8 kg/ha) to 306 pounds per acre (137.7 kg/ha) 2 years after a spring prescribed fire. Basal area and biomass of most needlegrasses are also often reduced following fire, with basal area commonly being reduced by as much as 50 percent [37]. Small needlegrass plants with a lower ratio of dead to living plant material and less fuel volume generally respond more favorably to fire than do larger plants [37]. Richardson needlegrass is nonrhizomatous; therefore postfire regeneration is through seed or sprouting by surviving plants [10]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Elimination of large scale fires has enabled coniferous forests to encroach into grassland habitats. Fire policy in Glacier National Park before 1972 favored the development of coniferous forests at the expense of fescue grasslands [16]. Fire policies should assure the preservation of vegetation types such as the fescue grassland, of which Richardson needlegrass is an important component [16].

REFERENCES

SPECIES: Achnatherum richardsonii | Richardson Needlegrass
REFERENCES : 1. Bezeau, L. M.; Johnston, A. 1962. In vitro digestibility of range forage plants of the Festuca scabrella association. Canadian Journal of Plant Science. 42: 692-697. [441] 2. Beetle, Alan A. 1977. Recognition of Artemisia subspecies--a necessity. In: Johnson, Kendall L., ed. Wyoming shrublands: Proceedings, 6th Wyoming shrub ecology workshop; 1977 May 24-25; Buffalo, WY. Laramie, WY: Shrub Ecology Workshop: 35-42. [419] 3. Bramble-Brodahl, Mary K. 1978. Classification of Artemisia vegetation in the Gros Ventre area, Wyoming. Moscow, ID: University of Idaho; 1978. 126 p. M.S. thesis. [506] 4. Dorn, Robert D. 1977. Flora of the Black Hills. [Place of publication unknown]: Robert D. Dorn and Jane L. Dorn. 377 p. [820] 5. Dorn, Robert D. 1984. Vascular plants of Montana. Cheyenne, WY: Mountain West Publishing. 276 p. [819] 6. Dorn, Robert D. 1988. Vascular plants of Wyoming. Cheyenne, WY: Mountain West Publishing. 340 p. [6129] 7. Eddleman, Lee; McLean, Alastair. 1969. Herbage--its production and use within the coniferous forests. In: Taber, Richard D., ed. Coniferous forests of the northern Rocky Mountains: Proceed. of the 1968 Symposium; 1968 September 17-20; Missoula, MT. Missoula, MT: University of Montana Foundation, Center for Natural Resources: 179-196. [7545] 8. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 9. 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] 10. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 11. Gruell, George E.; Brown, James K.; Bushey, Charles L. 1986. Prescribed fire opportunities in grasslands invaded by Douglas-fir: state-of-the-art guidelines. Gen. Tech. Rep. INT-198. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 19 p. [1050] 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. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 14. 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] 15. Johnston, A.; Bezeau, L. M. 1962. Chemical composition of range forage plants of the Festuca scabrella association. Canadian Journal of Plant Science. 42: 105-115. [1291] 16. Koterba, Wayne D.; Habeck, James R. 1971. Grasslands of the North Fork Valley, Glacier National Park, Montana. Canadian Journal of Botany. 49: 1627-1636. [6401] 17. 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] 18. 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] 19. Looman, J. 1969. The fescue grasslands of western Canada. Vegetatio. 19: 128-145. [1471] 20. 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] 21. 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] 22. Nimlos, Thomas J.; Van Meter, Wayne P.; Daniels, Lewis A. 1968. Rooting patterns of forest understory species as determined by radioiodine absorption. Ecology. 49(6): 1145-1151. [4120] 23. Van Dyne, George M.; Payne, Gene F., compilers. 1964. Grazing responses of western range plants. Bozeman, MT: Montana State College, Department of Animal and Range Sciences. 69 p. [2418] 24. Payne, Gene F. 1973. Vegetative rangeland types in Montana. Bull. 671. Bozeman, MT: Montana State University, Montana Agricultural Experiment Station. 15 p. [1847] 25. Pojar, J.; Trowbridge, R.; Coates, D. 1984. Ecosystem classification and interpretation of the sub-boreal spruce zone, Prince Rupert Forest Region, British Columbia. Land Management Report No. 17. Victoria, BC: Province of British Columbia, Ministry of Forests. 319 p. [6929] 26. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 27. Ross, Robert L.; Murray, Earl P.; Haigh, June G. 1973. Soil and vegetation inventory of near-pristine sites in Montana. Bozeman, MT: U.S. Department of Agriculture, Soil Conservation Service. 55 p. [2029] 28. Rydberg, P. A.; Shear, C. L. 1897. A report upon the grasses and forage plants of the Rocky Mountain Region. Bulletin No. 5. Washington, DC: U.S. Department of Agriculture, Division of Agrostology. 48 p. [5497] 29. Wheeler, W. A.; Hill, D. D. 1957. Grassland seeds. Princeton, NJ: D. Van Nostrand Company, Inc. 628 p. [18902] 30. Tyser, Robin W. 1990. Ecology of fescue grasslands in Glacier National Park. In: Boyce, Mark S.; Plumb, Glenn E., eds. National Park Service Research Center, 14th annual report. Laramie, WY: University of Wyoming, National Park Service Research Center: 59-60. [14766] 31. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 32. U.S. Department of Agriculture. 1948. Grass: The yearbook of agriculture 1948. Washington, DC. 892 p. [2391] 33. 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] 34. Wakimoto, Ronald H.; Willard, E. Earl. 1991. Monitoring post-fire vegetation recovery in ponderosa pine and sedge meadow communities in Glacier National Park, NW Montana. Research Joint Venture Agreement INT-89441. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 17 p. Progress Report. [17635] 35. Wright, Henry A.; Neuenschwander, Leon F.; Britton, Carlton M. 1979. The role and use of fire in sagebrush-grass and pinyon-juniper plant communities: A state-of-the-art review. Gen. Tech. Rep. INT-58. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Statio. 48 p. [2625] 36. 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] 37. Wright, Henry A.; Klemmedson, James O. 1965. Effect of fire on bunchgrasses of the sagebrush-grass region in southern Idaho. Ecology. 46(5): 680-688. [2624] 38. 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] 39. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090]

Index

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