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Introductory

SPECIES: Carex geyeri | Elk Sedge
ABBREVIATION : CARGEY SYNONYMS : NO-ENTRY SCS PLANT CODE : CAGE2 COMMON NAMES : elk sedge Geyer's sedge pine sedge TAXONOMY : The currently accepted scientific name for elk sedge is Carex geyeri Boott (Cyperaceae) [31]. There are no recognized subspecies, varieties, or forms. LIFE FORM : Graminoid FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : S. A. Snyder, July 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Snyder, S. A. 1992. Carex geyeri. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Carex geyeri | Elk Sedge
GENERAL DISTRIBUTION : Elk sedge occurs from southern Alberta and British Columbia south through eastern Washington, Oregon, and northern California. It occurs in western Montana and throughout Idaho south into Wyoming, Colorado, Utah, the western edge of Nevada, and into the northern portions of New Mexico and Arizona [31,53]. ECOSYSTEMS : FRES11 Spruce - fir FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES23 Fir - spruce FRES26 Lodgepole pine FRES29 Sagebrush FRES44 Alpine STATES : AZ CA CO HI ID MT NV NM OR UT WA WY AB BC ADMINISTRATIVE UNITS : BIHO BLCA CODA FOBU GLAC GRTE MEVE MORA NOCA ROMO TICA YELL BLM PHYSIOGRAPHIC REGIONS : 3 Southern Pacific Border 4 Sierra Mountains 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 KUCHLER PLANT ASSOCIATIONS : K005 Mixed conifer forest K008 Lodgepole pine - subalpine forest K011 Western ponderosa forest K012 Douglas-fir forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K020 Spruce - fir - Douglas-fir forest K021 Southwestern spruce - fir forest K022 Great Basin pine forest K038 Great Basin sagebrush K050 Fescue - wheatgrass SAF COVER TYPES : 206 Engelmann spruce - subalpine fir 208 Whitebark pine 210 Interior Douglas-fir 212 Western larch 213 Grand fir 217 Aspen 218 Lodgepole pine 219 Limber pine 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Elk sedge is dominant in the western habitat types, community types, and plant associations listed below. A preliminary description of plant communities found on the Sawtooth, White Cloud, Boulder, and Pioneer Mountains [42] Aspen community types of the Intermountain Region [37] Aspen community types of Utah [38] Coniferous forest habitat types of central and southern Utah [57] Coniferous forest habitat types of northern Utah [36] Forest habitat types of central Idaho [52] Forest habitats of eastern Idaho-western Wyoming [46] Forest habitat types of northern Idaho: A second approximation [11] Forest habitat types of Montana [40] Forest vegetation of the Arapaho and Roosevelt Natioanl Forest in central Colorado: A habitat type classification [11] Forest vegetation of the Medicine Bow National Forest in southeastern Wyoming: A habitat type classification [1] Forest vegetation of the Routt National Forest in northwestern Colorado: A habitat type classification [23] Forest vegetation of the White River National Forest in western Colorado: A habitat type classification [24] Habitat types on selected parts of the Gunnison and Uncompahgre National Forest [26] Plant associations and management guide for the gand fir zone, Gifford Pinchot National Forest [54] Plant communities of the Blue Mountains in eastern Oregon and southeastern Washington [19] Riparian classification for the Upper Salmon/Middle Fork Salmon River Drainages, Idaho [55] Sagebrush-grass habitat types of southern Idaho [22]

VALUE AND USE

SPECIES: Carex geyeri | Elk Sedge
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Elk sedge is an important spring and summer forage for elk [32]. It is also eaten by deer, bear, and livestock [31]. It has been rated as good forage for cattle, horse, and elk; and fair for sheep and deer [13,53]. PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : A food value study in western Montana showed that the total nonstructural carbohydrates (TNC) of elk sedge root crowns were lowest in spring and summer during leaf emergence, flowering, and fruiting [28]. Carbohydrate levels increased in late summer. TNC was greater on forested sites than on open sites. Food values during dormancy have been listed [39]: crude protein = 10.2 percent phosphorous = 0.18 percent calcium = 0.58 percent Stark [45] has listed elk sedge values for 11 nutrients. COVER VALUE : Elk sedge provides good cover for small mammals and nongame birds [13]. VALUE FOR REHABILITATION OF DISTURBED SITES : Because of its extensive root system and its ability to tolerate high soil temperatures and moisture stress, elk sedge has been used to revegetate severely eroded slopes of the Cascade Range in Oregon and Washington [25]. OTHER USES AND VALUES : Native Americans used elk sedge culms for food [53]. MANAGEMENT CONSIDERATIONS : Elk sedge decreases under heavy grazing pressure. Grazing trials in Oregon, Wyoming, and Idaho have shown reductions in cover and seed production with continued use [1,3,14,58]. Elk sedge recovers well following tree harvest [5]. A clearcut subalpine fir (Abies lasiocarpa) stand in Colorado showed an increase in elk sedge cover from 0.2 percent before harvest to 14.1 percent 5 years after harvest [12]. Chaining and spraying elk sedge can result in an initial increase followed by a decrease in production a few years later [30]. Elk sedge competes with pine seedlings following harvest [1].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Carex geyeri | Elk Sedge
GENERAL BOTANICAL CHARACTERISTICS : Elk sedge is a rhizomatous graminoid 6 to 12 inches (15-30 cm) tall [31]. Its clustered stems and scaley leaves remain green throughout the winter, until they are replaced with new leaves in early spring. Leaf blades are 0.04 to 0.12 inch (1-3 mm) wide and flat or channelled [53]. Elk sedge has a solitary spike with a dark brown flower head at the top. Its fruit is an achene. RAUNKIAER LIFE FORM : Chamaephyte Geophyte REGENERATION PROCESSES : Elk sedge reproduces mainly by rhizomes but also reproduces by seed [53]. Elk sedge usually produces only one seed per spike, and its viability is low [25]. Seeds can be stored in the soil for several decades and germinate following disturbance that opens up the canopy [27]. SITE CHARACTERISTICS : Elk sedge occurs from the foothills to subalpine and dry montane forests [31]. It occurs in a variety of habitats from mesic to dry and on all slopes and aspects. Elk sedge tends to occur more frequently on the dry phases of the wetter habitat types. Soil types vary from clay loam to gravelly, sandy loam and can be deep or shallow [38,40,52]. Parent materials include sandstone, shale, granite, andesite, rhyolite, and latite [21,52]. Elk sedge associates not listed under Distribution and Occurrence include Engelmann spruce (Picea engelmannii), common juniper (Juniperus communis), Rocky Mountain juniper (J. scopulorum), mountain big sagebrush (Artemisia tridentata ssp. vaseyana), rose (Rosa spp.), snowberry (Symphoricarpos spp.), chokecherry (Prunus spp.), pinegrass (Calamagrostis rubescens), lupine (Lupinus spp.), heartleaf arnica (Arnica cordifolia), and Fendler meadowrue (Thalictrum fendleri) [11,22,23,26,37,40]. Elevational ranges have been listed for elk sedge in some western states [13,52]: Idaho from 3,700 to 8,700 feet (1,128-2,652 m) Montana from 3,400 to 7,800 feet (1,036-2,377 m) Wyoming from 6,800 to 10,000 feet (2,073-3,048 m) Colorado from 6,000 to 11,000 feet (1,829-3,353 m) Utah from 6,000 to 10,800 feet (1,829-3,292 m) SUCCESSIONAL STATUS : Facultative Seral Species Elk sedge is a native, moderately shade-tolerant, cool-season, perennial graminoid 53]. It is listed as a dominant, climax ground cover in several western habitat types. The quaking aspen/chokecherry/elk sedge type of Utah can be climax or seral to the subalpine fir/Oregon grape type in northern Utah or the subalpine fir/elk sedge type in southern and central Utah [38]. The quaking aspen-lodgepole pine/elk sedge type in central Idaho is seral to the lodgepole pine/pinegrass type [37]. Elk sedge is an indicator of late seral stages of succession or the climax type on dry sites for several habitat types in Idaho [47,48,49,50,51]. In grand fir/beargrass (Xerophyllum tenax)-blue huckleberry (Vaccinium globulare) habitat types with an elk sedge layer group, elk sedge can be replaced by pinegrass, arnica, or beargrass as the overstory cover increases [43]. Elk sedge is an indicator of the wetter sites of the ponderosa pine series and an indicator of the lowest elevation lodgepole pine series in southeastern Wyoming habitat types [1]. Elk sedge also indicates the drier sites of the subalpine fir series in western Montana, as well as the coldest climatic conditions of the elk sedge phase within the subalpine fir/elk sedge habitat type [40]. In habitat types where elk sedge is the dominant ground cover species, it is often the first to sprout following fire [42]. It is also dominant in early successional stages following fire in spruce-fir habitat types of Colorado [10]. SEASONAL DEVELOPMENT : Elk sedge remains green throughout the winter, retaining its leaves until new ones emerge in the spring [28]. It is usually one of the first species to green up in the spring, using soil moisture and then going dormant as later species emerge [50]. It flowers from April through July in Montana [13].

FIRE ECOLOGY

SPECIES: Carex geyeri | Elk Sedge
FIRE ECOLOGY OR ADAPTATIONS : Elk sedge has rhizomes that allow it to survive fires [7]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Ground residual colonizer (onsite, initial community)

FIRE EFFECTS

SPECIES: Carex geyeri | Elk Sedge
IMMEDIATE FIRE EFFECT ON PLANT : Fire may top-kill elk sedge, but rhizomes, sometimes buried as as deep as 63 inches (160 cm) below the soil surface, usually survive [17,44]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : Following a clearcut and February broadcast burn in a Douglas-fir-dominated forest in central Idaho, elk sedge cover remained the same compared to cut but unburned sites [17]. Elk sedge was present in small amounts on this low-elevation site. On another higher site in the same drainage, elk sedge cover was significantly reduced on the broadcast burned sites compared to the unburned sites. (Burns were conducted in December). Cover on the burned sites was half that of cover on the unburned sites immediately following the burn and 2 and 5 years later. At postfire year 10 cover on the burned site was 60 percent of the unburned site. Elk sedge rhizomes may have been shallow in these areas, and the fire could have destroyed them [17]. An early August prescribed fire in a Douglas-fir forest of central Idaho drastrically reduced elk sedge frequency, from 52 percent to 12 percent, by the second post-fire year [33]. By the fourth year, elk sedge had increased to half of its prefire frequency and remained stable through the seventh postfire year. A prescribed burn in a mixed aspen-conifer forest in Idaho had little effect on elk sedge cover, which remained similar to that on the unburned sites [8]. PLANT RESPONSE TO FIRE : Elk sedge usually sprouts following fire and increases to form dense cover [2,7]. It can, however, decrease following fire if rhizomes are too close to the surface and become damaged [2,17]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Following a July wildfire in Waterfalls Canyon, Grand Teton National Park, elk sedge had a 50 percent frequency on moderately burned areas, and a 67 percent frequency on severely burned areas [4]. These figures were compared to a severe wildfire that burned 40 years earlier in an adjacent area. On the older burn elk sedge had a 58 percent frequency the 40th postfire year, compared to a 47 percent frequency on unburned sites. Elk sedge cover was high on all sites but was particularly abundant on the more recently burned site. A prescribed fire to improve elk winter range was conducted in July on the Clearwater National Forest, Idaho [32]. By the second growing season, frequency of elk sedge on burned areas almost doubled compared to unburned areas, where it remained stable. Some plots on the burned areas were seeded with elk sedge following the burn. Frequency doubled on these sites as well, but there was no significant difference in elk sedge response between the seeded and unseeded sites. Eight years following an August wildfire on the Bitterroot National Forest, Montana, elk sedge had an average of a 2 percent cover [34]. No prefire cover figures were given. FIRE MANAGEMENT CONSIDERATIONS : High-intensity broadcast burning is recommended in Douglas-fir/elk sedge habitat types in Idaho following clearcutting in order to promote natural regeneration of the same habitat type [18]. Periodic underburning in the Blue Mountains of Oregon has enhanced elk sedge subjected to grazing pressure [20]. Equations for estimating fuel loadings from ground cover and plant height have been developed for elk sedge [9].

REFERENCES

SPECIES: Carex geyeri | Elk Sedge
REFERENCES : 1. Alexander, Robert R.; Hoffman, George R.; Wirsing, John M. 1986. Forest vegetation of the Medicine Bow National Forest in southeastern Wyoming: a habitat type classification. Res. Pap. RM-271. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 39 p. [307] 2. Arno, Stephen F.; Simmerman, Dennis G.; Keane, Robert E. 1985. Forest succession on four habitat types in western Montana. Gen. Tech. Rep. INT-177. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 74 p. [349] 3. Austin, D. D.; Urness, Philip J. 1982. Vegetal responses and big game values after thinning regenerating lodgepole pine. Great Basin Naturalist. 42(4): 512-516. [8354] 4. Barmore, William J., Jr.; Taylor, Dale; Hayden, Peter. 1976. Ecological effects and biotic succession following the 1974 Waterfalls Canyon Fire in Grand Teton National Park. Research Progress Report 1974-1975. Unpublished report on file at: U.S. Department of Agriculture, Forest Service, Intermountain Fire Sciences Laboratory, Missoula, MT. 99 p. [16109] 5. Basile, Joseph V.; Jensen, Chester E. 1971. Grazing potential on lodgepole pine clearcuts in Montana. Res. Pap. INT-98. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 11 p. [8280] 6. 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] 7. Bradley, Anne F.; Noste, Nonan V.; Fischer, William C. 1991. Fire ecology of forests and woodlands in Utah. Gen. Tech. Rep. INT-287. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 128 p. [18211] 8. Brown, James K.; DeByle, Norbert V. 1989. Effects of prescribed fire on biomass and plant succession in western aspen. Res. Pap. INT-412. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 16 p. [9286] 9. Brown, James K.; Marsden, Michael A. 1976. Estimating fuel weights of grasses, forbs, and small woody plants. Res. Note INT-210. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest & Range Experiment Station. 11 p. [5030] 10. Clagg, Harry B. 1975. Fire ecology in high-elevation forests in Colorado. Fort Collins, CO: Colorado State University. 137 p. Thesis. [113] 11. Cooper, Stephen V.; Neiman, Kenneth E.; Roberts, David W. 1991. (Rev.) Forest habitat types of northern Idaho: a second approximation. Gen. Tech. Rep. INT-236. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 143 p. [14792] 12. Crouch, Glenn L. 1985. Effects of clearcutting a subalpine forest in central Colorado on wildlife habitat. Res. Pap. RM-258. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 12 p. [8225] 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. Driscoll, Richard S. 1957. Effects of intensity and date of herbage removal on herbage production of elk sedge. Journal of Range Management. 10: 212. [16142] 15. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 16. 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] 17. Geier-Hayes, Kathleen. 1989. Vegetation response to helicopter logging and broadcast burning in Douglas-fir habitat types at Silver Creek, central Idaho. Res. Pap. INT-405. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 24 p. [6810] 18. Geier-Hayes, Kathleen. 1991. Natural regeneration microsites for Douglas-fir in central Idaho. In: Baumgartner, David M.; Lotan, James E., compilers. Interior Douglas-fir: The species and its management: Symposium proceedings; 1991 February 27 - March 1; Spokane, WA. Pullman, WA: Washington State University, Cooperative Extension: 247-254. [18299] 19. Hall, Frederick C. 1973. Plant communities of the Blue Mountains in eastern Oregon and southeastern Washington. R6-Area Guide 3-1. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 82 p. [1059] 20. Hall, Frederick C. 1977. Ecology of natural underburning in the Blue Mountains of Oregon. R6-ECOL-79-001. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 11 p. [8481] 21. Hess, Karl; Alexander, Robert R. 1986. Forest vegetation of the Arapaho and Roosevelt National Forests in central Colorado: a habitat type classification. Res. Pap. RM-266. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 48 p. [1141] 22. Hironaka, M.; Fosberg, M. A.; Winward, A. H. 1983. Sagebrush-grass habitat types of southern Idaho. Bulletin Number 35. Moscow, ID: University of Idaho, Forest, Wildlife and Range Experiment Station. 44 p. [1152] 23. Hoffman, George R.; Alexander, Robert R. 1980. Forest vegetation of the Routt National Forest in northwestern Colorado: a habitat classification. Res. Pap. RM-221. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 41 p. [1179] 24. Hoffman, George R.; Alexander, Robert R. 1983. Forest vegetation of the White River National Forest in western Colorado: a habitat type classification. Res. Pap. RM-249. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 36 p. [1178] 25. Klock, G. O. 1969. Some autecological characteristics of elk sedge. Res. Note PNW-106. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 5 p. [15870] 26. Komarkova, Vera. 1986. Habitat types on selected parts of the Gunnison and Uncompahgre National Forests. Final Report Contract No. 28-K2-234. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 270 p. [1369] 27. Wallace, L.L.; Svejcar, T. 1987. Mycorrhizal and clipping effects on Andropogon gerardii photosynthesis. American Journal of Botany. 74(7): 1138-1142. [53] 28. Krueger, Janice K.; Bedunah, Donald J. 1988. Influence of forest site on total nonstructural carbohydrate levels of pinegrass, elk sedge, and snowberry. Journal of Range Management. 41(2): 144-149. [3532] 29. 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] 30. Kufeld, Roland C. 1983. Responses of elk, mule deer, cattle, and vegetation to burning, spraying and chaining of Gambel oak rangeland. Tech. Publ. 34. Fort Collins, CO: Colorado Division of Wildlife. 47 p. [253] 31. 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] 32. Leege, Thomas A.; Godbolt, Grant. 1985. Herebaceous response following prescribed burning and seeding of elk range in Idaho. Northwest Science. 59(2): 134-143. [1436] 33. Lyon, L. Jack. 1971. Vegetal development following prescribed burning of Douglas-fir in south-central Idaho. Res. Pap. INT-105. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 30 p. [1495] 34. Lyon, L. Jack. 1984. The Sleeping Child Burn--21 years of postfire change. Res. Pap. INT-330. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 17 p. [6328] 35. 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] 36. Mauk, Ronald L.; Henderson, Jan A. 1984. Coniferous forest habitat types of northern Utah. Gen. Tech. Rep. INT-170. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 89 p. [1553] 37. Mueggler, Walter F. 1988. Aspen community types of the Intermountain Region. Gen. Tech. Rep. INT-250. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 135 p. [5902] 38. Mueggler, Walter F.; Campbell, Robert B., Jr. 1986. Aspen community types of Utah. Res. Pap. INT-362. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 69 p. [1714] 39. Paulsen, Harold A., Jr. 1969. Forage values on a mountain grassland-aspen range in western Colorado. Journal of Range Management. 22: 102-107. [1842] 40. 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] 41. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 42. Schlatterer, Edward F. 1972. A preliminary description of plant communities found on the Sawtooth, White Cloud, Boulder and Pioneer Mountains. Unpublished report. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Region. 111 p. [2076] 43. Simpson, Michael L. 1990. The subalpine fir/beargrass habitat type: Succession and management. Moscow, ID: University of Idaho. 134 p. Thesis. [13464] 44. Spence, Liter E. 1937. Root studies of important range plants of the Boise River watershed. Journal of Forestry. 35: 747-754. [77] 45. Stark, N. 1983. The nutrient content of Rocky Mountain vegetation: a handbook for estimating nutrients lost through harvest and burning. Misc. Publ. 14. Missoula, MT: University of Montana, School of Forestry, Montana Forest and Conservation Experiment Station. 81 p. [8617] 46. Steele, Robert; Cooper, Stephen V.; Ondov, David M.; [and others]. 1983. Forest habitat types of eastern Idaho-western Wyoming. Gen. Tech. Rep. INT-144. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 122 p. [2230] 47. Steele, Robert; Geier-Hayes, Kathleen. 1987. The grand fir/blue huckleberry habitat type in central Idaho: succession and management. Gen. Tech. Rep. INT-228. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 66 p. [8133] 48. Steele, Robert; Geier-Hayes, Kathleen. 1989. The Douglas-fir/mountain maple habitat type in central Idaho: succession and management. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 77 p. Preliminary draft. [8434] 49. Steele, Robert; Geier-Hayes, Kathleen. 1989. The Douglas-fir/ninebark habitat type in central Idaho: succession and management. Gen. Tech. Rep. INT-252. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 65 p. [8136] 50. Steele, Robert; Geier-Hayes, Kathleen. 1990. The Douglas-fir/pinegrass habitat type in central Idaho: Succession and management. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 155 p. Review draft. [15764] 51. Steele, Robert; Geier-Hayes, Kathleen. 1992. The grand fir/mountain maple habitat type in central Idaho: succession and management. Gen. Tech. Rep. INT-284. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 90 p. [17791] 52. Steele, Robert; Pfister, Robert D.; Ryker, Russell A.; Kittams, Jay A. 1981. Forest habitat types of central Idaho. Gen. Tech. Rep. INT-114. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 138 p. [2231] 53. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 54. Topik, Christopher. 1989. Plant association and management guide for the grand fir zone, Gifford Pinchot National Forest. R6-Ecol-TP-006-88. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 110 p. [11361] 55. Tuhy, Joel S.; Jensen, Sherman. 1982. Riparian classification for the Upper Salmon/Middle Fork Salmon River drainages, Idaho. Smithfield, UT: White Horse Associates. Final Report, Contract with U.S.S. Forest Service, Region 4. 153 p. [8380] 56. 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] 57. Youngblood, Andrew P.; Mauk, Ronald L. 1985. Coniferous forest habitat types of central and southern Utah. Gen. Tech. Rep. INT-187. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 89 p. [2684] 58. Zimmerman, G. T.; Neuenschwander, L. F. 1984. Livestock grazing influences on community structure, fire intensity, and fire frequency within the Douglas-fir/ninebark habitat type. Journal of Range Management. 37(2): 104-110. [10103] 59. 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]

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