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Introductory

SPECIES: Rosa woodsii | Wood's Rose
ABBREVIATION : ROSWOO SYNONYMS : NO-ENTRY SCS PLANT CODE : ROWO COMMON NAMES : Wood's rose common wild rose wild rose mountain rose TAXONOMY : The currently accepted scientific name for Wood's rose is Rosa woodsii Lindl. Recognized varieties are as follows [28,39,44]: R. woodsii var. woodsii R. woodsii var. fendleri (Crep.)Rydb. R. woodsii var. ultramontana (Wats.)Jeps. R. woodsii var. glabrata (Parish)Cole R. woodsii var. gratissima (Greene)Cole LIFE FORM : Shrub FEDERAL LEGAL STATUS : See OTHER STATUS OTHER STATUS : Wood's rose is considered rare within the Guadalupe Mountains National Park, Texas, but is common elsewhere in Texas [49]. COMPILED BY AND DATE : Julie L. Tesky, July 1992. LAST REVISED BY AND DATE : AUTHORSHIP AND CITATION : Tesky, Julie L. 1992. Rosa woodsii. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Rosa woodsii | Wood's Rose
GENERAL DISTRIBUTION : Wood's rose occurs from Minnesota west and northwest to Alaska and British Columbia, south to Arizona, northern Mexico and western Texas and north to western Kansas and North Dakota [24,39,44]. It is the most widespread native rose in Alberta [24]. ECOSYSTEMS : FRES11 Spruce - fir FRES17 Elm - ash - cottonwood FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir - spruce FRES24 Hemlock - Sitka spruce FRES25 Larch FRES26 Lodgepole 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 FRES44 Alpine STATES : AK AZ CA CO ID IA KS MN MT NE NV NM ND OK OR SD TX UT WA AB BC MB NT ON SK MEXICO ADMINISTRATIVE UNITS : AGFO ARCH BADL BAND BIHO BICA BLCA BRCA CACH CANY CARE CEBR CHIR COLM CODA CRMO DEVA DETO DINO FLFO FOBU GLAC GLCA GRCA GRTE GRKO GRBA GRSA GUMO JODA KICA LAVO LABE MEVE MORA MORU NABR NOCA ROMO SAGU SEQU SUCR THRO TICA WACA WHIS WICA YELL YOSE YUCH ZION 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 : K001 Spruce - cedar - hemlock forest K002 Cedar - hemlock - Douglas-fir forest K003 Silver fir - Douglas-fir forest K004 Fir - hemlock forest K005 Mixed conifer forest K008 Lodgepole pine - subalpine forest K009 Pine - cypress forest K010 Ponderosa shrub forest K011 Western ponderosa forest 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 K019 Arizona pine forest K020 Spruce - fir - Douglas-fir forest K021 Southwestern spruce - fir forest K022 Great Basin pine forest K023 Juniper - pinyon woodland K024 Juniper steppe woodland K025 Alder - ash forest K026 Oregon oakwoods K027 Mesquite bosque K028 Mosaic of K002 and K026 K029 California mixed evergreen forest K030 California oakwoods K031 Oak - juniper woodlands K032 Transition between K031 and K037 K033 Chaparral K034 Montane chaparral K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K052 Alpine meadows and barren K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K059 Trans-Pecos shrub savanna K065 Grama - buffalograss K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlegrass K068 Wheatgrass - grama - buffalograss K069 Bluestem - grama prairie K071 Shinnery K074 Bluestem prairie K075 Nebraska Sandhills prairie K081 Oak savanna K085 Mesquite - buffalograss K086 Juniper - oak savanna K088 Fayette prairie K098 Northern floodplain forest K100 Oak - hickory forest SAF COVER TYPES : 40 Post oak - blackjack oak 42 Bur oak 43 Bear oak 44 Chestnut oak 45 Pitch pine 46 Eastern redcedar 50 Black locust 52 White oak - black oak - northern red oak 53 White oak 55 Northern red oak 57 Yellow-poplar 58 Yellow-poplar - eastern hemlock 59 Yellow-poplar - white oak - northern red oak 61 River birch - sycamore 62 Silver maple - American elm 64 Sassafras - persimmon 65 Pin oak - sweetgum 201 White spruce 202 White spruce - paper birch 203 Balsam poplar 204 Black spruce 206 Engelmann spruce - subalpine fir 209 Bristlecone pine 210 Interior Douglas-fir 211 White fir 215 Western white pine 216 Blue spruce 217 Aspen 218 Lodgepole pine 220 Rocky Mountain juniper 222 Black cottonwood - willow 229 Pacific Douglas-fir 230 Douglas-fir - western hemlock 233 Oregon white oak 234 Douglas-fir - tanoak - Pacific madrone 235 Cottonwood - willow 236 Bur oak 237 Interior ponderosa pine 238 Western juniper 239 Pinyon - juniper 240 Arizona cypress 241 Western live oak 242 Mesquite 243 Sierra Nevada mixed conifer 244 Pacific ponderosa pine - Douglas-fir 245 Pacific ponderosa pine 246 California black oak 247 Jeffrey pine 248 Knobcone pine 249 Canyon live oak 250 Blue oak - Digger pine 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 : Wood's rose is commonly dominant or codominant on riparian and wetland sites [7,14,22,23,32]. Extensive stands of Wood's-rose-dominated community types are found along the Missouri and Yellowstone rivers in Montana [22]. Published classifications listing Wood's rose as a dominant or codominant are as follows: Classification and management of riparian and wetland sites in northwestern Montana. [7] Ecology and distribution of riparian vegetation in the Trout Creek Mountains of southeastern Oregon. [14] Riparian dominance types of Montana. [23] Classification and management of riparian and wetland sites in central and eastern Montana. [22] Preliminary riparian community type classification for Nevada. [32]

VALUE AND USE

SPECIES: Rosa woodsii | Wood's Rose
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Wood's rose is browsed by livestock and big game from spring through fall. Moderate use by mule deer and elk has been reported [24]. Game and livestock strongly prefer this shrub in the spring when the leaves appear [37]. Porcupines and beavers also browse the leaves [21]. Wood's rose hips persist on the plant through much of the winter. Many birds and mammals are sustained by these dry fruits when the ground is covered with snow [37,50]. In Cache Valley, Utah, Wood's rose hips provide a high-energy food for wintering mule deer [47]. Rose hips are a favorite food of squirrels [21]. Wood's rose hips are sometimes eaten by coyotes and bears [21,31]. PALATABILITY : Livestock and big game find Wood's rose leaves palatable from spring through fall [50]. The palatability of Wood's rose to livestock and wildlife species in several western states has been rated as follows [11]: CO MT ND UT WY Cattle Fair Fair Fair Poor Fair Sheep Good Fair Fair Fair Fair Horses Poor Poor Poor Poor Fair Pronghorn ---- ---- ---- Fair Good Elk ---- Poor ---- Good Good Mule deer ---- Fair ---- Good Good White-tailed deer Good Good ---- ---- Fair Small mammals ---- Good ---- Good Good Small nongame birds ---- Good ---- Good Good Upland game birds ---- Good Good Good Good Waterfowl ---- ---- Poor ---- Poor NUTRITIONAL VALUE : Wood's rose leaves are considered fair to good livestock forage, particularly for sheep [23]. In North Dakota, the protein content of leaves and twigs combined were found to be sufficent to meet the maintenance requirements of sheep and cattle during the growing season. Calcium percentages met the requirements for sheep and cattle for the entire year [12]. In the Black Hills of South Dakota, Wood's rose leaves contained good phosphorus percentages in the spring and retained adequate levels into the fall. However, the stems of rose were below the 0.16 percent phosphorous level recommended as minimal for pregnant ewes. Stems were slightly deficient in phosphorous requirement during the winter [10]. Of the species studied, Wood's rose produced the greatest amount of dry matter, but because of lower digestibility and crude protein content, it will probably not support as many deer per unit area as other browse species on the site [10]. Wood's rose hips are a high source of digestible energy. Digestible energy levels in the diet of deer might be increased by planting rose stock that produces heavy crops of hips [47]. Rose hips are moderately high in crude protein during winter [17]. COVER VALUE : The dense thickets formed by Wood's rose along field borders and stream courses are used for nesting and escape cover by many birds and small mammals [20,21,24]. The degree to which Wood's rose provides environmental protection during one or more seasons for wildlife species has been rated as follows [11]: CO MT ND UT WY Pronghorn ---- ---- ---- Fair Poor Elk ---- ---- ---- Fair Poor Mule deer ---- ---- ---- Fair Fair White-tailed deer Fair Good ---- ---- ---- Small mammals Good Fair ---- ---- ---- Small nongame birds Good Fair ---- Good Good Upland game birds ---- Fair Good Good Good Waterfowl ---- Good Poor ---- Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Wood's rose extensive rhizomes, and good survivability and revegetation characteristics even on harsh sites makes this species an effective tool in erosion control [7,24,27]. It has also been suggested as a useful species for revegetation on high pH and lime soils [24]. Wood's rose is used to revegetate disturbed sites along streambanks and seeps, and shows promise for road cut revegetation in western Montana and northern Idaho [7,27]. Following planting on a road cut, Wood's rose increased by sprouting from the roots to the extent that it became difficult to distinguish individual plants. The proliferation of flowers and fruits observed on Wood's rose indicate that establishment of new plants from seed may also occur [27]. Of the species studied, Wood's rose demonstrated the best survivability and regeneration characteristics [27]. Wood's rose also appears to be a good species to plant with seeded grasses on untreated acid mine spoils in California. The survival and growth of Wood's rose was not reduced by grass competition [15]. Good results have been obtained with hardwood cuttings, direct seeding and transplanting trials. Native seed is available [17,24]. OTHER USES AND VALUES : Native americans made extensive use of Wood's rose roots, stems, leaves, flowers, and hips for foods and therapeutic materials. The hips are a source of vitamin C and are dried for use in flavoring teas, jellies, fruitcakes, and puddings [24,35,50]. The flowers provide a source of pollen for honey bees [50]. Wood's rose is used as an ornamental near homes to attract birds and other wildlife [50]. MANAGEMENT CONSIDERATIONS : Wood's rose has a fairly high tolerance to browsing. It is susceptible to various leaf spots, as well as to leaf rusts, gray mold, powdery mildew, common gall, and stem cankers [21,24]. The principal forest insect pests of Rosa spp. are California tent caterpillar (Malacasoma californicum), rose leaf hopper (Edwardsiana rosae), and a subspecies of western tussock moth (Orgyia vetusta spp. gulosa) [21].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Rosa woodsii | Wood's Rose
GENERAL BOTANICAL CHARACTERISTICS : Wood's rose is a native, cool-season, fast-growing, long-lived perennial bushy shrub [1,24,39,41]. It attains a height of 1.5 to 6 feet (0.5-1.8 m). The stems have prickles which are straight or slightly curved and 0.2 to 0.3 inch (0.06-0.09 m) long [44]. The leaves are from 0.8 to 2.4 inches (2-6 cm) long [39,41]. Wood's rose has rhizomes and shallow, fibrous roots that branch frequently [26]. RAUNKIAER LIFE FORM : Phanerophyte Chamaephyte Geophyte REGENERATION PROCESSES : Sexual reproduction: Rosa spp. generally first flower and produce seed when they are 2 to 5 years old. Good crops are usually produced every 2 years. Seeds of Wood's rose are injested with the fruit and dispersed in the droppings of birds and mammals [21]. The seeds have a seed coat dormancy and require warm or cold stratification. Seed viability ranged from 44 to 64 percent for seed collected in northern Alberta [24]. The seeds remain viable for 2 to 5 years [45]. Seeds will germinate within 30 to 40 days [24,45]. Vegetative reproduction: Wood's rose spreads vegetatively through underground rhizomes, sprouting from the root crown, and layering [24,50]. SITE CHARACTERISTICS : Wood's rose occurs on bluffs, dry grassy slopes, and on sandhills throughout the prairies. It is also found on riverbanks and clearings in boreal and subalpine forests [6,24,39,42]. It is common on disturbed sites throughout the eastern slopes of the Rocky mountains and is especially prevalent along roadsides and south-facing cutbanks [24]. Wood's rose is found throughout the Great Basin but prefers rather moist sites along streams or in seepage areas along fences. When conditions are favorable, nearly impenetrable thickets of Wood's rose are formed along some mountain streams [35]. Soils: Wood's rose is adapted to a wide range of soil types and textures. Growth is generally best on moderately fertile, well-drained clay loam, sandy loam, or sandy soils [11,21]. It is also adapted to a broad range of moisture conditions but tends to favor moist, well-drained soils that are present in riparian ecosystems [21]. Wood's rose is tolerant of moderately acid to weakly basic soils [23]. Shade tolerance: Wood's rose flourishes in moderate shade to full sunlight and therefore grows well on all aspects [6]. Climate: Wood's rose is seldom found where the average annual precipitation is less than 12 inches (260 mm) [6]. It is variable in hardiness and climatic tolerance. It will grow in moderate climates as well as alpine environments, which suggests that some plants can tolerate a cold, snowy climate with a short growing season [13,21]. Elevational range: The elevational range of Wood's rose in several western states is as follows [11]: Utah: 3,500 to 7,500 feet (1,062-2,275 m) Colorado: 3,500 to 11,700 feet ((1,062-3,549 m) Wyoming: 4,000 to 8,300 feet (1,213-2,518 m) Montana: 3,500 to 6,600 feet (1,062-2,002 m) Associated species: Wood's rose is commonly found associated with the following species: western snowberry (Symphoricarpos occidentalis), common chokecherry (Prunus virginiana), hawthorn (Crataegus spp.), serviceberry (Amelanchier alnifolia), Kentucky bluegrass (Poa pratensis), fowl bluegrass (P. palustris), quackgrass (Agropyron repens), big sagebrush (Artemisia tridentata), western river alder (Alnus incana), virginsbower (Clematis ligusticifolia), golden currant (Ribes aureum), coyote willow (Salix exigua), cheatgrass (Bromus tectorum), beardless wildrye (Elymus triticoides), sweet scented bedstraw (Galium triflorum), quaking aspen (Populus tremuloides), and Canada thistle (Cirsium arvense) [7,14,22,23,32]. SUCCESSIONAL STATUS : Wood's rose is an aggressive pioneer of abandoned fields, disturbed sites, gullies, and land cuts and fills [23,26]. It is moderately shade tolerant and therefore can persist as an understory species in mid-seral to climax communities. In northwestern Montana, Wood's-rose-dominated community types represent a disturbance-induced seral stage of the ponderosa pine/red-osier dogwood (Pinus ponderosa/Cornus stolenifera) and Douglas-fir (Pseudotsuga menziesii)/red-osier dogwood habitat types [7]. In many cases Wood's rose occurs as a dominant or codominant understory species within stands dominated by cottonwood (Populus spp.), ponderosa pine, and Douglas-fir [23]. Additionally, in the Black Hills of South Dakota, Wood's rose occurs as part of the dominant vegetation in the subclimax chaparral which occurs as an intermediate zone along the eastern foothills, between the mixed prairie and the montane forest and eastward along the stream valleys [25]. SEASONAL DEVELOPMENT : Wood's rose generally flowers from late spring to midsummer. However, date of flowering varies considerably according to elevation and exposure [21,35]. The rose hips ripen during late summer and fall [35]. Hips generally remain on the plant throughout the winter [35,50].

FIRE ECOLOGY

SPECIES: Rosa woodsii | Wood's Rose
FIRE ECOLOGY OR ADAPTATIONS : Wood's rose is moderately fire tolerant and is usually favored by low-severity fire. It can persist after low- to moderate-severity fire because of its ability to sprout from undamaged or buried root crowns and rhizomes [7,21]. It occasionally germinates from on-site or off-site seed sources after fire [51]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud rootcrown Rhizomatous shrub, rhizome in soil Ground residual colonizer (onsite, initial community) Initial-offsite colonizer (offsite, initial community) Secondary colonizer - offsite seed

FIRE EFFECTS

SPECIES: Rosa woodsii | Wood's Rose
IMMEDIATE FIRE EFFECT ON PLANT : Wood's rose is typically top-killed by fire [2,3,4,48]. Root crowns and underground rhizomes survive low- or moderate-severity fires [7,21]. However, the shallow root crowns of Wood's rose are susceptible to injury, and populations consequently decrease following high-severity fire [3,21]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : PLANT RESPONSE TO FIRE : Wood's rose recovery varies with fire severity. Top-killed plants will sprout from the root crown and underground surviving rhizomes [9,17,34,52]. Reproduction from seed is rarely observed after fire. When seedlings are observed in a burn area, their rate of growth is slow compared to that of other species [51]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : In, Wood's rose doubled in abundance by postfire year 2 [33]. Following a moderate- to high-severity fire at Manning Basin northeast of Montpelier, Idaho, Wood's rose recovered to near preburn densities by postfire year 2 [8]. The first growing season after a spring burn in an aspen-conifer stand, west Boulder River, Montana, the density per acre of Wood's rose showed significant increase. The average height for Wood's rose following the first postburn growing season was about half or less of their average preburn height [19]. One year following a high-severity fire in a northern Arizona ponderosa pine forest, postfire biomass of Wood's rose was only about 0.25 that of prefire levels [46]. FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Rosa woodsii | Wood's Rose
REFERENCES : 1. Anderson, J. P. 1959. Flora of Alaska and adjacent parts of Canada. Ames, IA: Iowa State University Press. 543 p. [9928] 2. Anderson, Murray L.; Bailey, Arthur W. 1979. Effect of fire on a Symphoricarpos occidentalis shrub community in central Alberta. Canadian Journal of Botany. 57: 2820-2823. [2867] 3. Bartos, Dale L. 1979. Effects of burning on the aspen ecosystem. In: Johnson, Kendall L., ed. Wyoming shrublands: Proceedings of the 8th shrub ecology workshop; 1979 May 30-31; Jackson, WY. Laramie, WY: University of Wyoming, Division of Range Management, Wyoming Shrub Ecology Workshop: 47-58. [400] 4. Bartos, Dale L.; Mueggler, Walter F. 1979. Influence of fire on vegetation production in the aspen ecosystem in western Wyoming. In: Boyce, Mark S.; Hayden-Wing, Larry D., eds. North American elk, ecology, behavior and management. Laramie, WY: University of Wyoming: 75-78. [5101] 5. 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] 6. Blauer, A. Clyde; Plummer, A. Perry; McArthur, E. Durant; [and others]. 1975. Characteristics and hybridization of important Intermountain shrubs. I. Rose family. Res. Pap. INT-169. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 36 p. [472] 7. 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] 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. Conrad, C. Eugene. 1987. Common shrubs of chaparral and associated ecosystems of southern California. Gen. Tech. Rep. PSW-99. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station. 86 p. [4209] 10. Dietz, Donald R. 1972. Nutritive value of shrubs. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., tech. eds. Wildland shrubs--their biology and utilization: An international symposium; Proceedings; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 289-302. [801] 11. 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] 12. Erickson, D. O.; Barder, W. T.; Wanapat, S.; Williamson, R. L. 1981. Nutritional composition of common shrubs in North Dakota. Proceedings, North Dakota Academy of Science. 35: 4. [6454] 13. Erlanson, Eileen Whitehead. 1934. Experimental data for a revision of the North American wild roses. Botanical Gazette. 96(2): 197-259. [12434] 14. Evenden, Angela G. 1989. Ecology and distribution of riparian vegetation in the Trout Creek Mountains of southeastern Oregon. Corvallis, OR: Oregon State University. 156 p. Dissertation. [10231] 15. Everett, Richard L.; Meeuwig, Richard O.; Butterfield, Richard I. 1980. Revegetation of untreated acid spoils Leviathan mine, Alpine County, California. California Geology. 32(1): 8-10. [895] 16. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 17. Ferguson, Robert B. 1983. Use of rosaceous shrubs for wildland plantings in the Intermountain West. In: Monsen, Stephen B.; Shaw, Nancy, compilers. Managing Intermountain rangelands--improvement of range and wildlife habitats; Proceedings of symposia; 1981 September 15-17; Twin Falls, ID; 1982 June 22-24; Elko, NV. Gen. Tech. Rep. INT-157. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 136-149. [915] 18. 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] 19. Gordon, Floyd A. 1976. Spring burning in an aspen-conifer stand for maintenance of moose habitat, West Boulder River, Montana. In: Proceedings, Montana Tall Timbers fire ecology conference and Intermountain Fire Research Council fire & land management symposium; 1974 October 8-10; Missoula, MT. No. 14. Tallahassee, FL: Tall Timbers Research STation: 501-538. [13529] 20. 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] 21. Haeussler, S.; Coates, D.; Mather J. 1990. Autecology of common plants in British Columbia: A literature review. Economic and Regional Development Agreement FRDA Rep. 158. Victoria, BC: Forestry Canada, Pacific Forestry Centre; British Columbia Ministry of Forests, Research Branch. 272 p. [18034] 22. 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] 23. Hansen, Paul L.; Chadde, Steve W.; Pfister, Robert D. 1988. Riparian dominance types of Montana. Misc. Publ. No. 49. Missoula, MT: University of Montana, School of Forestry, Montana Forest and Conservation Experiment Station. 411 p. [5660] 24. 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] 25. Hayward, Herman E. 1928. Studies of plants in the Black Hills of South Dakota. Botanical Gazette. 85(4): 353-412. [1110] 26. Horton, Howard, ed. and compiler. 1989. Interagency forage and conservation planting guide for Utah. Extension Circular 433. Logan, UT: Utah State University, Cooperative Extension Service. 67 p. [12231] 27. Hungerford, Roger D. 1984. Native shrubs: suitability for revegetating road cuts in northwestern Montana. Res. Pap. INT-331. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 13 p. [1220] 28. 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] 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. 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] 31. Mace, Richard D.; Bissell, Gael N. 1986. Grizzly bear food resources in the flood plains and avalanche chutes of the Bob Marshall Wilderness, Montana. In: Contreras, Glen P.; Evans, Keith E., compilers. Proceedings--grizzly bear habitat symposium; 1985 April 30 - May 2; Missoula, MT. Gen. Tech. Rep. INT-207. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 78-91. [10812] 32. Manning, Mary E.; Padgett, Wayne G. 1989. Preliminary riparian community type classification for Nevada. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Region. 135 p. Preliminary draft. [11531] 33. Miller, Melanie. 1976. Shrub sprouting response to fire in a Douglas-fir/western larch ecosystem. Missoula, MT: University of Montana. 124 p. Thesis. [8945] 34. Mitchell, Jerry M. 1984. Fire management action plan: Zion National Park, Utah. Record of Decision. 73 p. Report on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. [17278] 35. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 342 p. [1702] 36. Parker, Karl G. 1975. Some important Utah range plants. Extension Service Bulletin EC-383. Logan, UT: Utah State University. 174 p. [9878] 37. Plummer, A. Perry; Christensen, Donald R.; Monsen, Stephen B. 1968. Restoring big-game range in Utah. Publ. No. 68-3. Ephraim, UT: Utah Division of Fish and Game. 183 p. [4554] 38. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 39. Stephens, H. A. 1973. Woody plants of the North Central Plains. Lawrence, KS: The University Press of Kansas. 530 p. [3804] 40. Stromberg, Julie C.; Patten, Duncan T. 1989. Early recovery of an eastern Sierra Nevada riparian system after 40 years of stream diversion. In: Abell, Dana L., technical coordinator. Proceedings of the California riparian systems conference: Protection, management, and restoration for the 1990's; 1988 September 22-24; Davis, CA. Gen. Tech. Rep. PSW-110. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 399-404. [13770] 41. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 42. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 43. 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] 44. Vines, Robert A. 1960. Trees, shrubs, and woody vines of the Southwest. Austin, TX: University of Texas Press. 1104 p. [7707] 45. Vories, Kimery C. 1981. 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Index

Related categories for Species: Rosa woodsii | Wood's Rose

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