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Introductory

SPECIES: Spiraea douglasii | Douglas' Spirea
ABBREVIATION : SPIDOU SYNONYMS : NO-ENTRY SCS PLANT CODE : SPDO SPDOD SPDOM COMMON NAMES : Douglas' spirea hardhack pink spirea TAXONOMY : The currently accepted scientific name of Douglas' spirea is Spiraea douglasii Hook. [20,35]. There are two recognized varieties: S. d. var. douglasii (Douglas' spirea) [21,25] S. d. var. menziesii (Hook.) Presl (Menzies' spirea) [21,25,35] Douglas' spirea may hybridize with white spiraea (S. betulifolia) to form pyramid spirea (S. x pyramidata Greene) [33,35]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Lora L. Esser, May 1995 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Esser, Lora L. 1995. Spiraea douglasii. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Spiraea douglasii | Douglas' Spirea
GENERAL DISTRIBUTION : Douglas' spirea occurs from Alaska south to northern California and east to western Montana [21,29,35]. Pyramid spirea occurs from British Columbia south to Oregon and east to western Montana [35]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir-spruce FRES24 Hemlock-Sitka spruce FRES26 Lodgepole pine FRES27 Redwood FRES28 Western hardwoods STATES : AK CA ID MT OR WA BC ADMINISTRATIVE UNITS : CODA CRLA FOCL MORA MOSA NOCA OLYM BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 4 Sierra Mountains 5 Columbia Plateau 8 Northern Rocky Mountains 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 K006 Redwood forest K007 Red fir forest K010 Ponderosa shrub forest K011 Western ponderosa forest K012 Douglas-fir forest K013 Cedar-hemlock-pine forest K025 Alder-ash forest K026 Oregon oakwoods K028 Mosaic of K002 and K026 SAF COVER TYPES : 205 Mountain hemlock 206 Engelmann spruce-subalpine fir 207 Red fir 210 Interior Douglas-fir 211 White fir 215 Western white pine 217 Aspen 218 Lodgepole pine 221 Red alder 222 Black cottonwood-willow 223 Sitka spruce 224 Western hemlock 225 Western hemlock-Sitka spruce 226 Coastal true fir-hemlock 227 Western redcedar-western hemlock 228 Western redcedar 229 Pacific Douglas-fir 230 Douglas-fir-western hemlock 232 Redwood 233 Oregon white oak 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : 203 Riparian woodland 422 Riparian HABITAT TYPES AND PLANT COMMUNITIES : Douglas' spirea occurs mainly in riparian habitats such as swamps, mud flats, shrub carrs, marshes, bogs, and along streams [8,17,18,23,44]. In British Columbia Douglas' spirea is found in rush (Juncus spp.)-sedge (Carex spp.)-quillwort (Isoetes spp.) and shrub carr community types [8,18]. Common associates include Rocky Mountain maple (Acer glabrum), Sitka willow (Salix sitchensis), salmonberry (Rubus spectabilis), salal (Gaultheria shallon), sweet gale (Myrica gale), and bog rush (Juncus effusus) [2,28]. In Washington a Douglas' spirea-bog blueberry (Vaccinium uliginosum)/sedge community type is described. Common associates include swordleaf rush (Juncus ensifolius), blister sedge (Carex vesicaria), Sitka sedge (C. sitchensis), slough sedge (C. obnupta), common willowweed (Epilobium glandulosum), and kneeling angelica (Angelica genuflexa) [19]. Douglas' spirea is also a member of a field horsetail (Equisetum arvense)-skunkcabbage (Veratrum californicum) swamp association. Associates include Sitka alder (Alnus viridis ssp. sinuata), black twinberry (Lonicera involucrata), and red-osier dogwood (Cornus sericea) [16]. Associates of Douglas' spirea in Washington and Oregon forest commuities include dwarf huckleberry (Vaccinium caespitosum), blue wildrye (Elymus glaucus), deer fern (Blechnum spicant), bracken fern (Pteridium aquilinum), western yarrow (Achillea millefolium), widefruit sedge (Carex eurycarpa), Wood's rose (Rosa woodsii), and bristly black currant (Ribes lacustre) [12,29,30]. In California Douglas' spirea occurs in sphagnum bog, north coast riparian scrub, and freshwater marsh communities [23,44]. Common associates include bigleaf maple (Acer macrophyllum), Pacific wax-myrtle (Myrica californica), Hooker willow (Salix hookeriana), Hinds willow (S. hindsiana), sedge (Carex spp.), bear sedge (C. arcta), round-leaved sundew (Drosera rotundifolia), and coast Labrador tea (Ledum glandulosum var. columbiana) [23,44]. In eastern Idaho and western Montana, Douglas' spirea is dominant in herbaceous wetland communities [41,42]. In Montana a Douglas' spirea community type has been described [4,17]. Douglas' spirea is dominant in a thinleaf alder community type [4]. Common associates in Montana include Booth willow (Salix boothii), Geyer willow (S. geyeriana), Wood's rose, western polemonium (Polemonium occidentale), beaked sedge (Carex rostrata), inflated sedge (C. vesicaria), reed canarygrass (Phalaris arundinacea), and creeping bentgrass (Agrostis stolonifera) [4,17]. The following publications list Douglas' spirea as a community dominant: Classification and management of riparian and wetland sites in northwestern Montana [4] Riparian dominance types of Montana [17] Plant association and management guide: Willamette National Forest [19] Riparian zone associations: Deschutes, Ochoco, Fremont, and Winema National Forests [29] Classification of aquatic and semiaquatic wetland natural areas in Idaho and western Montana [41] Management of riparian vegetation in the northcoast region of California's coastal zone [44]

VALUE AND USE

SPECIES: Spiraea douglasii | Douglas' Spirea
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Douglas' spirea has limited value as livestock forage because of typically dense stands, high water tables, and scarcity of palatable grasses [4,17]. It is sometimes eaten by livestock in the summer and fall [4,17]. In western Washington and Oregon Douglas' spirea is browsed by black-tailed deer [5,8]. PALATABILITY : In Oregon Douglas' spirea has a low palatability rating [29]. NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : In Washington a breeding population of long-billed marsh wrens was found nesting in a Douglas' spirea emergent shrub community type [52]. In British Columbia Douglas' spirea is a component of the western hemlock-Sitka spruce habitat type which is important grizzly bear habitat [2]. In Oregon quaking aspen-lodgepole pine/Douglas' spirea/widefruit sedge and lodgepole pine/Douglas' spirea/widefruit sedge habitat types are utilized by livestock for bedding and shade. These two habitat types are also important to deer, elk, and raptors [29]. VALUE FOR REHABILITATION OF DISTURBED SITES : Carlson [6] recommends Douglas' spirea for riparian revegetation programs in the Pacific Northwest. In a black cottonwood (Populus trichocarpa) riparian community, Douglas' spirea seedlings were planted in the fall of 1980 and had a 27 percent survival rate. In 1988 percent cover of Douglas' spirea had increased [6]. In Oregon Douglas' spirea was propagated as in situ hardwood cuttings (collected and planted on-site the same day) in a Pacific silver fir (Abies amabilis) community [48]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : In Oregon Douglas' spirea is sensitive to trampling and soil compaction [4,32]. The riparian lodgepole pine/Douglas' spirea/forb association has been overgrazed in Oregon. Douglas' spirea may be eliminated with continued overuse [29].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Spiraea douglasii | Douglas' Spirea
GENERAL BOTANICAL CHARACTERISTICS : Douglas' spirea is a rhizomatous, deciduous shrub with erect, spreading stems 3 to 6 feet (1-1.8 m) tall [17,35,40]. Leaves are 1 to 4 inches (3-10 cm) long [20,35]. Seeds are 0.08 inch (2 mm) long [40]. Douglas'spirea forms adventitious roots after burial [1]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Douglas' spirea is a rhizomatous shrub that often forms dense colonies [1,4,32]. It will sprout from the stem base and root crown following disturbance [4,29]. In Washington following the May 18, 1980 volcanic eruption of Mount St. Helens, Douglas' spirea showed extensive rhizome development in the tephra (volcanic aerial ejecta) and contained one to five adventitious roots per centimeter of stem 1 year after burial. Maximum adventitious root length of Douglas' spirea was 3.6 inches (9 cm) [1]. Douglas' spirea produces small seeds that are probably dispersed via animals and strong winds [40]. SITE CHARACTERISTICS : Douglas' spirea occurs in riparian areas including wet meadows, floodplains, terraces, bogs, swamps, and along streams, rivers, lakes, springs, and ponds [4,12,17,23,24]. Douglas' spirea grows best on moist to semiwet soils with good drainage [20,28,29,32,35]. It grows best on loam and sandy loam soils, but occurs on silty clay, clay loam, and gravelly substrates as well [17,19,23,29,42]. Douglas' spirea is tolerant of permanently water-logged soils (peat) and widely fluctuating water tables [23,28]. Elevations for Douglas' spirea are as follows: feet meters California 4,620-6,435 1,400-1,950 [20,46] Montana 3,760-6,700 1,147-2,044 [4,35] Oregon 2,200-5,800 660-1,740 [29] Washington 2,500-5,000 750-1,500 [19] SUCCESSIONAL STATUS : Douglas' spirea occurs mostly in seral communities [2,4,7,27,37]. It is generally shade intolerant [28], but horticultural specimens have been described as shade tolerant [11,20]. In British Columbia Douglas' spirea is a pioneer species in disclimax communities maintained by avalanches [2]. In southwestern British Columbia and northwestern Washington, Douglas' spirea is a pioneer species on clearcut sites [27,37]. In northwestern Montana a Douglas' spirea community type may be seral to an as yet undefined thinleaf alder/Douglas' spirea habitat type [4]. Douglas' spirea often forms dense impenetrable thickets in riparian areas [4]. In Washington Douglas' spirea usually occurs in mosaics with other hydric and mesic non-forest species in riparian forest openings [19]. SEASONAL DEVELOPMENT : In California Douglas' spirea flowers from June to September [40].

FIRE ECOLOGY

SPECIES: Spiraea douglasii | Douglas' Spirea
FIRE ECOLOGY OR ADAPTATIONS : Douglas' spirea is moderately resistant to fire [32] and sprouts readily from the stem base and rhizomes after fire [4,17,29,32]. In presettlement times, wildfires were "probably common" in Douglas' spirea communities of riparian areas in Montana and Oregon; soils were usually dry by mid-summer, allowing fires from adjacent uplands to encroach upon the stand [17,29]. Fires were probably infrequent in the thinleaf alder-Douglas' spirea association in Oregon [29]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown Rhizomatous shrub, rhizome in soil

FIRE EFFECTS

SPECIES: Spiraea douglasii | Douglas' Spirea
IMMEDIATE FIRE EFFECT ON PLANT : Douglas' spirea is probably topkilled by most fires and killed by severe fires. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : The literature contains few reports describing Douglas' spirea after fire. Because of its sprouting ability, it probably survives most fires. In central British Columbia Douglas' spirea was present with shinyleaf spirea (Spiraea betulifolia var. lucida) in seral Engelmann spruce (Picea engelmannii)-fir (Abies spp.) stands. Relative density of the Spiraea spp. in plots 4 to 22 years after fire was 4 percent; in plots 37 to 75 years after fire, it was 9 percent [13]. In British Columbia McMinn [38] studied a site in a western hemlock/Sitka spruce forest burned in 1861 and again in 1931. By 1948 Douglas' spirea had formed dense thickets with salmonberry and thimbleberry. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Spiraea douglasii | Douglas' Spirea
REFERENCES : 1. Antos, Joseph A.; Zobel, Donald B. 1985. Plant form, developmental plasticity and survival following burial by volcanic tephra. Canadian Journal of Botany. 63: 2083-2090. [12553] 2. Banner, Allen; Pojar, Jim; Trowbridge, Rick; Hamilton, Anthony. 1986. Grizzly bear habitat in the Kimsquit River Valley, coastal British Columbia: classification, description, and mapping. 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: 36-49. [10810] 3. 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] 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. Brown, Ellsworth R. 1961. The black-tailed deer of western Washington. Biological Bulletin No. 13. [Place of publication unknown]: Washington State Game Commission. 124 p. [8843] 6. Carlson, Jack R. 1992. Selection, production, and use of riparian plant materials for the western United States. In: Landis, Thomas D., technical coordinator. Proceedings, Intermountain Forest Nursery Association; 1991 August 12-16; Park City, UT. Gen. Tech. Rep. RM-211. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 55-67. [20926] 7. Cates, Rex G.; Orians, Gordon H. 1975. Successional status and the palatability of plants to generalized herbivores. Ecology. 56: 410-418. [15989] 8. Cowan, Ian McTaggart. 1945. The ecological relationships of the food of the Columbian black-tailed deer, Odocoileus hemionus columbianus (Richardson), in the c. forest region southern Vancouver Island, British Columbia. Ecological Monographs. 15(2): 110-139. [16006] 9. Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information network (PIN) data base: Colorado, Montana, North Dakota, Utah, and Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 786 p. [806] 10. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 11. 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] 12. Franklin, Jerry F.; Dyrness, C. T. 1973. Natural vegetation of Oregon and Washington. Gen. Tech. Rep. PNW-8. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 417 p. [961] 13. Garman, E. H. 1929. Natural reproduction following fires in central British Columbia. Forestry Chronicle. 5: 28-44. [20224] 14. 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] 15. Habeck, James R. 1961. The original vegetation of the mid-Willamette Valley, Oregon. Northwest Science. 35: 65-77. [11419] 16. Miller, Richard E.; Fowler, Norma L. 1994. Life history variation and local adaptation within two populations of Bouteloua rigidiseta (Texas grama). Journal of Ecology. 82: 855-864. [24502] 17. 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] 18. Harcombe, Andrew; Pendergast, Bruce; Petch, Bruce; Janz, Doug. 1983. Elk habitat management: Salmon River Valley. MOE Working Report 1. 83-05-10. Victoria, BC: Ministry of the Environment. 83 p. [9984] 19. Hemstrom, Miles A.; Logan, Sheila E.; Pavlat, Warren. 1987. Plant association and management guide: Willamette National Forest. R6-Ecol 257-B-86. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 312 p. [13402] 20. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of California. Berkeley, CA: University of California Press. 1400 p. [21992] 21. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 22. Hoffman, George R. 1960. The small mammal components of six climax plant associations in eastern Washington and northern Idaho. Ecology. 41(3): 571-572. [12472] 23. Holland, Robert F. 1986. Preliminary descriptions of the terrestrial natural communities of California. Sacramento, CA: California Department of Fish and Game. 156 p. [12756] 24. Hulten, Eric. 1968. Flora of Alaska and neighboring territories. Stanford, CA: Stanford University Press. 1008 p. [13403] 25. Kartesz, John T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II--thesaurus. 2nd ed. Portland, OR: Timber Press. 816 p. [23878] 26. Kellman, M. C. 1969. Plant species interrelationships in a secondary succession in coastal British Columbia. Syesis. 2: 201-212. [6589] 27. Klinka, K.; Scagel, A. M.; Courtin, P. J. 1985. Vegetation relationships among some seral ecosystems in southwestern British Columbia. Canadian Journal of Forestry. 15: 561-569. [5985] 28. Klinka, K.; Krajina, V. J.; Ceska, A.; Scagel, A. M. 1989. Indicator plants of coastal British Columbia. Vancouver, BC: University of British Columbia Press. 288 p. [10703] 29. Kovalchik, Bernard L. 1987. Riparian zone associations: Deschutes, Ochoco, Fremont, and Winema National Forests. R6 ECOL TP-279-87. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 171 p. [9632] 30. Kovalchik, Bernard L.; Chitwood, Lawrence A. 1990. Use of geomorphology in the classification of riparian plant associations in mountainous landscapes of central Oregon, U.S.A. Forest Ecology and Management. 33/34: 405-418. [6830] 31. Kovalchik, Bernard L.; Elmore, Wayne. 1992. Effects of cattle grazing systems on willow-dominated plant associations in central Oregon. In: Clary, Warren P.; McArthur, E. Durant; Bedunah, Don; Wambolt, Carl L., compilers. Proceedings--symposium on ecology and management of riparian shrub communities; 1991 May 29-31; Sun Valley, ID. Gen. Tech. Rep. INT-289. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 111-119. [19104] 32. Kovalchik, Bernard L.; Hopkins, William E.; Brunsfeld, Steven J. 1988. Major indicator shrubs and herbs in riparian zones on National Forests of central Oregon. R6-ECOL-TP-005-88. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Region. 159 p. [8995] 33. Kruckeberg, Arthur R. 1977. Manzanita (Arctostaphylos) hybrids in the Pacific Northwest: effects of human and natural disturbance. Systematic Botany. 2(4): 233-250. [13561] 34. 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] 35. 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] 36. LePage, P.; Pollack, J. C.; Coates, K. D. 1991. Chemical and manual control of thimbleberry (Rubus parviflorus) in northwestern British Columbia: a rate and timing trial. Western Journal of Applied Forestry. 6(4): 99-102. [16224] 37. Long, James N. 1977. Trends in plant species diversity associated with development in a series of Pseudotsuga menziesii/Gaultheria shallon stands. Northwest Science. 51(2): 119-130. [10152] 38. McMinn, Robert G. 1951. The vegetation of a burn near Blaney Lake, British Columbia. Ecology. 32(1): 135-140. [16498] 39. McNeil, Robert Curlan. 1975. Vegetation and fire history of a ponderosa pine - white fir forest in Crater Lake National Park. Corvallis, OR: Oregon State University. 171 p. Thesis. [5737] 40. Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA: University of California Press. 1905 p. [6155] 41. Rabe, Fred W.; Chadde, Steve W. 1994. Classification of aquatic and semiaquatic wetland natural areas in Idaho and western Montana. Natural Areas Journal. 14(3): 175-187. [23962] 42. Rabe, Fred W.; Elzinga, Caryl; Breckenridge, Roy. 1994. Classification of meandering glide and spring stream natural areas in Idaho. Natural Areas Journal. 14(3): 188-202. [23961] 43. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 44. Ray, Dan; Woodroof, Wayne; Roberts, R. Chad. 1984. Management of riparian vegetation in the northcoast region of California's coastal zone. In: Warner, Richard E.; Hendrix, Kathleen M., eds. California riparian systems: Ecology, conservation, and productive management: Proceedings of a conference; 1981 September 17-19; Davis, CA. Berkeley, CA: University of California Press: 660-672. [5867] 45. Roach, A. W. 1952. Phytosociology of the Nash Crater lava flows, Linn County, Oregon. Ecological Monographs. 22: 169-193. [8759] 46. Sawyer, John O.; Thornburgh, Dale A. 1977. Montane and subalpine vegetation of the Klamath Mountains. In: Barbour, Michael G.; Major, Jack, eds. Terrestrial vegetation of California. New York: John Wiley & Sons: 699-732. [685] 47. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. [23362] 48. Slagle, Kevin; Wilson, Mark Griswold. 1992. Revegetation efforts accompany campsite rehabilitation in a Pacific silver fir plant community. Restoration & Management Notes. 10(1): 82-83. [20624] 49. 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] 50. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. [23104] 51. U.S. Department of the Interior, National Biological Survey. [n.d.]. NP Flora [Data base]. Davis, CA: U.S. Department of the Interior, National Biological Survey. [23119] 52. Verner, Jared. 1975. Avian behavior and habitat management. In: Smith, Dixie R, technical coordinator. Proceedings of the symposium on management of forest and range habitats for nongame birds; 1975 May 6-9; Tucson, AZ. Gen. Tech. Rep. WO-1. Washington, DC: U.S. Department of Agriculture, Forest Service: 39-58. [17767] 53. Volland, Leonard A. 1974. Relation of pocket gophers to plant communities in the pine region of central Oregon. In: Black, Hugh C., ed. Wildlife and forest management in the Pacific Northwest: Proceedings of a symposium; 1973 September 11-12; Corvallis, OR. Corvallis, OR: Oregon State University, School of Forestry, Forest Research Laboratory: 149-166. [8003]

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