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Introductory

SPECIES: Salix exigua | Sandbar Willow
ABBREVIATION : SALEXI SYNONYMS : Salix argophylla Nutt. Salix fluviatilis var. exigua (Nutt.) Sarg. Salix interior Rowlee Salix interior var. angustissima (Anderss.) Dayton Salix interior var. exterior Fern. Salix interior var. pedicellata (Anderss.) Ball Salix interior var. wheeleri Rowlee Salix longifolia Muhl. non Lam. Salix longifolia var. angustissima Anderss. Salix longifolia var. argophylla (Nutt.) Anderss. Salix longifolia var. exigua (Nutt.) Bebb Salix longifolia var. pedicellata Anderss. Salix stenophylla Rydb. SCS PLANT CODE : SAEX COMMON NAMES : sandbar willow sand-bar willow coyote willow dusky willow narrowleaf willow slender willow basket willow acequia willow gray sandbar willow silvery desert willow TAXONOMY : There has been considerable disagreement over the taxonomy of the Salix exigua complex. Entities in this complex have been interpreted variously as distinct species [1,15,16] or as subspecies [7,10,22,27,62]. However, because the Salix exigua complex has many forms and freely interbreeding intermediates, ranking entities at the subspecific level appears to be more correct. The fully documented scientific name of sandbar willow is Salix exigua Nutt. Recognized subspecies and varieties [7,10,22,27,62], and a proposed variety [10] are: Salix exigua ssp. exigua var. exigua var. stenophylla ssp. interior var. pedicellata var. interior ssp. melanopsis var. melanopsis var. tenerrima (Brunsfeld and Johnson 1985) LIFE FORM : Tree FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Ronald Uchytil/March 1989 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Uchytil, Ronald J. 1989. Salix exigua. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Salix exigua | Sandbar Willow
GENERAL DISTRIBUTION : Sandbar willow occurs from eastern Quebec and New Brunswick west across Canada to central Manitoba, Yukon Territory, and central Alaska, south through British Columbia and Washington to southern California, and southeast to southern Texas, southern Louisiana, western Tennessee, Kentucky, and Virginia [8,35]. The ranges of subspecies exigua and interior overlap. Subspecies exigua is found from British Columbia, Montana, and the Black Hills south to New Mexico, Arizona, and Texas. Subspecies interior is found from New Brunswick to Alaska, south to Maine, Virginia, Kentucky, Lousiana, Arkansas, and New Mexico [22,54]. ECOSYSTEMS : FRES10 White - red - jack pine FRES11 Spruce - fir FRES15 Oak - hickory FRES17 Elm - ash - cottonwood FRES18 Maple - beech - birch FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES26 Lodgepole pine FRES28 Western hardwoods FRES29 Sagebrush FRES34 Chaparral - mountain shrub FRES38 Plains grasslands FRES39 Prairie STATES : AK AZ AR CA CO ID KS KY LA ME MI MN MO MT NE NV NM ND OK OR SD TN TX UT VA WA WI WY AB BC MB NB PQ YT MEXICO ADMINISTRATIVE UNITS : AGFO APIS ARCH BADL BAND BITH BICA BLRI BRCA BUFF CACH CANY CARE CEBR CHCU COLM CODA CRMO CUVA DEVA DEWA DINO EFMO FLFO FOBO GATE GLAC GLCA GRCA GRTE GRKO GRBA INDU JODA LAME LAMR MACA MEVE NABR PEFO PIRO PIPE ROMO SAGU SLBE THRO TICA WICA YELL YOSE YUCH ZION BLM PHYSIOGRAPHIC REGIONS : 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 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 K019 Arizona pine forest K020 Spruce - fir - Douglas-fir forest K023 Juniper - pinyon woodland K033 Chaparral K035 Coastal sagebrush K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K039 Blackbrush K040 Saltbush - greasewood K041 Creosotebush K042 Creosotebush - bursage K049 Tule marshes K051 Wheatgrass - bluegrass K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K057 Galleta - threeawn shrubsteppe K063 Foothills prairie K064 Grama - needlegrass - wheatgrass K065 Grama - buffalograss K066 Wheatgrass - needlegrass K070 Sandsage - bluestem prairie K075 Nebraska Sandhills prairie K093 Great Lakes spruce - fir forest K095 Great Lakes pine forest K098 Northern floodplain forest K106 Northern hardwoods SAF COVER TYPES : 1 Jack pine 5 Balsam fir 16 Aspen 63 Cottonwood 108 Red maple 202 White spruce - paper birch 210 Interior Douglas-fir 217 Aspen 218 Lodgepole pine 222 Black cottonwood - willow 235 Cottonwood - willow SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Sandbar willow usually occurs in early seral communities. These are typically riparian and occur as narrow bands immediately adjacent to the stream or river edge. Throughout the Rocky Mountain States, it commonly occurs as a dense shrub layer adjacent to bottomlands of cottonwood (Populus spp.) and birch (Betula spp.) [23,31,60]. Published classifications listing sandbar willow as an indicator or dominant in community types (cts), habitat types (hts), plant associations (pas), riparian site types (rst), or riparian zone associations (rzas) are presented below: Area Classification Authority sw US riparian hts Szaro & Patton 1987 sw US wetland cts Brown 1979 AZ,NM riparian pas Pase & Layser 1977 c CO: Arapaho & forest hts Hess & Alexander 1986 Roosevelt NFs CO: Gunnison & forest hts Komarkova & others 1988 Uncompahgre NFs e CO: South Platte riparian cts Lindauer 1983 & Arkansas Rivers e ID,w WY riparian cts Youngblood & others 1985a ID: Upper & Middle riparian cts Platts & others 1987 Forks Salmon River sw MT riparian veg. rst, hts, cts Hansen & others 1988 MT riparian dominance types Hansen & others 1988 sw NM riparian cts Medina 1986 sc OK bottomland cts Petranka & Holland 1980 OR: Deschutes, riparian cts Kovalchik 1987 Ochoco,Fremont & Winema NFs n UT,s ID riparian cts Padgett & others 1985

VALUE AND USE

SPECIES: Salix exigua | Sandbar Willow
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Sandbar willow is an important food source for many wildlife species. In the Great Basin it has been reported as a favorite food of beaver [41]. Willows (Salix spp.) in general are a preferred food of moose, and sandbar willow occurs in riparian and flood plain habitats which these animals frequent [6,30,34,45]. It also is browsed heavily by elk [45] but is of only slight improtance as browse for mule deer [57]. Dense stands provide hiding cover for wildlife but at the same time limit access for livestock [23,24]. Stands in eastern Colorado are used extensively by waterfowl during winter [35]. PALATABILITY : Van Dersal [57], reported that sandbar willow is relished by livestock. In the West, willows are generally considered to be more palatable to sheep than to cattle, but cattle may make greater use of willow plants because they tend to frequent riparian areas [56]. Most willows are highly palatable to moose, especially in winter, and make up a high percentage of their diet on western ranges [45]. The palatablity of sandbar willow to livestock and wildlife species in several western states has been rated as follows [14,51,53,29]: CA CO UT WY Cattle poor fair fair ---- Sheep fair fair fair ---- Horses poor fair fair ---- Moose ---- ---- ---- good Mule deer fair ---- good ---- White-tailed deer fair ---- ---- ---- NUTRITIONAL VALUE : Sandbar willow's energy value is rated as fair and its protein value as poor [14]. COVER VALUE : Sandbar willow can form stands or thickets several meters thick, with densely spaced stems. These stands provide excellent hiding cover for numerous wildlife species [23]. In California, the endangered Least Bell's Vireo frequently nests in willow thickets [21]. The degree to which sandbar willow provides environmental protection during one or more seasons for wildlife species has been rated as follows [14,18]: UT WY MT Pronghorn fair poor ---- Elk fair fair ---- Mule deer good good ---- White-tailed deer ---- good ---- Small mammals fair good ---- Small nongame birds good good ---- Upland game birds good good ---- Waterfowl fair good good VALUE FOR REHABILITATION OF DISTURBED SITES : Sandbar willow's ability to rapidly colonize disturbed sites makes it very useful for streambank stabilization projects. Cuttings are preferred for use in revegetating disturbed riparian areas because they quickly stabilize disturbed alluvium, which allows other plants to become established. Unrooted willow stem cuttings (slips) should be planted on sites that provide sufficient moisture to start and maintain growth through the growing season [56]. Since willows are sensitive to both competition and shading, dense tall grasses will reduce transplant survival [47] and may need to be removed by cutting or by herbicide application [34]. Although harder to plant, rooted stock is recommended because it has higher survival rates [47,58]. Slips should be obtained from local native stands. Cuttings should be planted 12 inches (30 cm) deep, with 8 inches (20 cm) left above ground [47]. Planting deep allows for more rooting surface to extract soil moisture and higher amounts of carbohydrates as stored food reserves [47,58]. Sandbar willow cuttings root along the entire length of the stem, with roots appearing in about 10 days [23,47]. If serious streambank erosion has caused a nearly verticle cut bank, reshaping of the slope may be needed to enhance success of transplants; reshaping is not necessary if, through protective measures, existing vegetation is able to stabilize the site [47,58]. Under any method of revegetation, sites should be fenced to protect them from grazing and trampling. OTHER USES AND VALUES : All willows produce salicin, which chemically is closely related to acetylsalicylic acid, commonly known as aspirin. This is probably why Native Americans used various preparations from willows to treat toothache, stomach ache, diarrhea, dysentery, and dandruff [41]. Native Americans also used the stems for basketry and bow making, and the bark for tea and fabric making [34]. MANAGEMENT CONSIDERATIONS : Stands of sandbar willow should be maintained because they help stabilize streambanks and protect them from erosion. Once degredation occurs, streambanks may erode rapidly [23].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Salix exigua | Sandbar Willow
GENERAL BOTANICAL CHARACTERISTICS : Sandbar willow is a short-lived deciduous shrub or small tree up to about 26 feet (8 m) tall, with soft weak wood, and thin gray-green to brown bark [7,54,62]. Staminate and pistillate flowers occur on separate plants as catkins. The fruit is a narrowly ovoid capsule. The three subspecies as a whole are characterized as (1) having numerous slender stems, (2) forming thickets through the underground spread of root suckers, and (3) having long and narrow mature leaves (5 to 20 times as long as wide) which are equally green on both surfaces [7,10,23]. The three subspecies intergrade, making identification difficult; general botanical characteristics of the subspecies include [7,10,16,54,62]: ssp. exigua ssp. interior ssp. melanopsis Mature Height 6-12 f (2-4 m) 20 feet (6 m) 12 feet (4 m) Mature Leaves lanceolate linear-lanceolate linear or oblong entire/few toothed remotely dentate toothed/subentire up to 13 cm long up to 12 cm long up to 12 cm long Male Catkins 1-4.5 cm long 3-4 cm long 1.5-3.5 cm long Female Catkins 1.5-6 cm long 2.5-3 cm long 2-4 cm long Capsule 4-7 mm long 6-7.3 mm long 3-5 mm long sessile pedicellate/glab. sessile/glabrous Twigs of Season thin-dense sparse-moderate pubescence,with pubescence,with strait appressed loosely appressed hairs wavy/curly hairs RAUNKIAER LIFE FORM : Undisturbed State: Phanerophyte (nanophanerophyte) Undisturbed State: Phanerophyte (microphanerophyte) Burned State: Hemicryptophyte REGENERATION PROCESSES : Sandbar willow is able to reproduce vegetatively by sprouting from underground shoot buds which occur on lateral roots and produce male or female clones. This method of vegetative reproduction (suckering) is uncommon in willows and occurs only in section Longifoliae [1]. Suckering allows this plant to spread and form colonies or thickets that may be several meters in diameter [1,10]. On a sandbar in Wisconsin estimated to be approximately 45 to 50 years old, more than 97 percent of sandbar willow (ssp. interior) stems sampled were clones 1 to 3 years old [3]. Regeneration may also occur through broken pieces of stems and roots which are transported and deposited by floodwaters and later sprout. This is a common method of vegetative reproduction in willows and may be important in initial colonization of some disturbed sites, although seeding seems to be more important [65]. Reproduction occurs sexually through the production of numerous seeds. Flowers are pollinated by insects, commonly by bees [41]. After fertilization, a capsule develops which eventually splits open, dispersing the numerous tiny seeds which are covered with a cottony down which aids in their dispersal by wind and water [2,41]. The nondormant seeds have a thin seed coat and germinate soon after being dispersed. On adequate substrates most germinate within 24 hours [12]. Ware and Penfound [59] found that seeds older than 1 week rarely germinated; thus seeds must land on suitable sites quickly if they are to germinate. Seeds kept at 32 to 41 degrees F (0-5 deg C) can be stored 4 to 6 weeks [8]. Seeds require light for germination [8]. Fresh alluvium deposited along rivers provides an ideal substrate for establishment. These sites have constant soil moisture and generally have no overstory trees to shade out this light-sensitive species [23]. SITE CHARACTERISTICS : Sandbar willow is found almost exclusively in riparian habitats, occupying banks of major rivers and smaller streams, lakes and ponds, marshy areas, alluvial terraces, and ditches [16,23,54,64]. It characteristically forms zones immediately adjacent to the water's edge. These areas are subjected to periodic flooding which often deposits sand and cobble below the high water mark. With severe annual flooding it may be the only shrub to survive in this zone [10]. Although often found below the high water mark, it must have a portion of its crown out of the water during part of the summer to survive [52]. Sandbar willow may also occur on moist, well-drained benches and bottomlands [10]. It normally does not exist in the understory due to its shade intolerance, and is generally replaced by cottonwoods. Soils: Sandbar willow occurs on a wide range of soil textures, but usually occurs on soils derived from alluvial or fluvial parent material of mixed geologic origin [60]. In western Montana it is typically found on coarse-textured substrates of sand or gravel, but in eastern Montana it may occur on fine-textured silts [23]. It also occurs on a wide range of soil types in eastern Idaho and western Wyoming. Sandbar willow communities there occupied soils from fine-loamy or finer textures, to coarse-textured soils with up to 35 percent rock fragments [64]. Associates: Adjacent drier areas may be dominated by cottonwoods, green ash (Fraxinus pennsylvanica), water birch (Betula occidentalis), thinleaf alder (Alnus incana ssp. tenuifolia), and other willows [23,64]. Elevation: Sites in the Intermountain West are typically at low to mid-elevations. Stands in Montana, Wyoming, and Idaho are adjacent to uplands commonly dominated by conifers, and big sagebrush (Artemisia tridentata) and Idaho fescue (Festuca idahoensis) [10,24,43,64]. Elevational ranges for several western states are presented below [10,14,24,25,42,42,48,62]: 2,700-8,500 feet (825-2,590 m) in UT 5,000-9,000 feet (1,524-2,743 m) in CO 8,000 feet (2,438 m) in s CA 3,200-6,700 feet (975-2,042 m) in MT 3,400-8,600 feet (1,036-2,621 m) in WY ssp. exigua: below 6,000 feet (1,830 m) in east-central ID ssp. melanopsis: 6,000-7,000 feet (1,830-2,130 m) in ec ID ssp. exigua: 3,500 to 3,900 feet (1,067-1,181 m) Trans Pecos TX ssp. interior: 1,800 to 3,600 feet (549-1,097 m) Trans Pecos TX SUCCESSIONAL STATUS : Sandbar willow is a pioneer species that colonizes new sand and gravel bars. After initial colonization, it helps stabilize the sand and gravel deposits, which allows other species to follow [49]. It may dominate these disturbed areas for only a few years before being replaced by cottonwoods. Repeated flooding may allow sandbar willow to persist [24], but once cottonwoods become established it cannot regenerate and establish itself. In Kansas, it occurs only as a pioneer; stands there maintain themselves for about 10 years before cottonwood becomes established and shades them out [4]. SEASONAL DEVELOPMENT : Catkins of sandbar willow develop over a several weeks, with the first expanding with the leaves and then continuing to develop as the leaves mature [10]. Flowering times for several states follow [14]: State Flowering Begins Flowering Ends CO May July MT May July UT April July WY May July Noble [67] reported that in Minnesota seeds were shed from early June to late July, which is commonly the time the rivers are dropping in elevation and exposing moist substrates favorable for germination. Seed dispersal probably coincides with local flooding patterns. In Oklahoma Ware and Penfound [59] reported that plants produce leaves by March 28, fruits by May 5, and seedlings by May 15.

FIRE ECOLOGY

SPECIES: Salix exigua | Sandbar Willow
FIRE ECOLOGY OR ADAPTATIONS : Sandbar willow sprouts from its roots after fire [11,50,65]. Its numerous wind-dispersed seeds are also important in revegetating burned areas [50]. The high soil and fuel moisture content characteristic of its steamside habitat reduces the chance of fire ingition and spread. POSTFIRE REGENERATION STRATEGY : survivor species; on-site surviving root crown or caudex off-site colonizer; seed carried by wind; postfire years one and two off-site colonizer; seed carried by animals or water; postfire yr 1&2

FIRE EFFECTS

SPECIES: Salix exigua | Sandbar Willow
IMMEDIATE FIRE EFFECT ON PLANT : Most fires kill only aboveground plant parts. However, severe fires can completely remove organic soil layers, leaving willow roots exposed and charred, thus eliminating basal sprouting [4,5,6]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Generally sandbar willow will sprout from its roots following fire [50,65]. Irwin [30] found that sandbar willow was common in the boreal forest of northeastern Minnesota 2 years after a May wildfire. Sandbar willow is a prolific seeder; off-site plants are important as a seed source for revegetating burned areas [65]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Due to its proximity to water or high water tables, sandbar willow communities may serve as natural fire breaks [2].

REFERENCES

SPECIES: Salix exigua | Sandbar Willow
REFERENCES : 1. Argus, George W. 1973. The genus Salix in Alaska and the Yukon. Publications in Botany, No. 2. Ottowa, ON: National Museums of Canada, National Museum of Natural Sciences. 279 p. [6167] 2. Arno, Stephen F.; Hammerly, Ramona P. 1977. Northwest trees. Seattle, WA: The Mountaineers. 222 p. [4208] 3. Barnes, W. J. 1985. Population dynamics of woody plants on a river island. Canadian Journal of Botany. 63: 647-655. [2855] 4. Bellah, R. Glenn; Hulbert, Lloyd C. 1974. Forest succession on the Republican River floodplain in Clay County, Kansas. Southwestern Naturalist. 19(2): 155-166. [241] 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. Boyd, Raymond J.; Cooperrider, Allen Y.; Lent, Peter C.; Bailey, James A. 1986. Ungulates. In: Cooperrider, Allen Y.; Boyd, Raymond J.; Stuart, Hanson R., eds. Inventory and monitoring of wildlife habitat. Denver, CO: U.S. Department of the Interior, Bureau of Land Management, Service Center: 519-564. [10856] 7. Brayshaw, T. Christopher. 1976. Catkin bearing plants of British Columbia. Occas. Pap. No. 18. Victoria, BC: The British Columbia Provincial Museum. 176 p. [6170] 8. Brinkman, Kenneth A. 1974. Salix L. willow. In: Schopmeyer, C. S., technical coordinator. Seeds of woody plants in the United States. Agric. Handb. 450. Washington, DC: U.S. Department of Agriculture, Forest Service: 746-750. [5412] 9. Brown, David E. 1979. Southwestern wetlands - their classification and characteristics. In: Johnson, R. Roy; McCormick, J. Frank, technical coordinators. Strategies for protection and management of floodplain wetlands & other riparian ecosystems: Proc. of the symposium; 1978 December 11-13; Callaway Gardens, GA. Gen. Tech. Rep. WO-12. Washington, DC: U.S. Department of Agriculture, Forest Service: 269-282. [4366] 10. Brunsfeld, Steven J.; Johnson, Frederic D. 1985. Field guide to the willows of east-central Idaho. Bulletin Number 39. Moscow, ID: University of Idaho; College of Forestry, Wildlife and Range Sciences; Forest, Wildlife and Range Experiment Station. 82 p. [6175] 11. 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] 12. Densmore, Roseann; Zasada, John. 1983. Seed dispersal and dormancy patterns in northern willows: ecological and evolutionary significance. Canadian Journal of Botany. 61: 3207-3216. [5027] 13. Dirschl, German J.; Dabbs, Don L.; Gentle, Garry C. 1974. Landscape classification and plant successional trends in the Peace-Athabasca Delta. Canadian Wildlife Service Report Series 30. 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Management of subalpine forests: building on 50 years of research: Proceedings of a technical conference; 1987 July 6-9; Silver Creek, CO. Gen. Tech. Rep. RM-149. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 167-172. [3475] 19. 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] 20. Geyer, Wayne A. 1989. Biomass yield potential of short-rotation hardwoods in the Great Plains. Biomass. 20: 167-175. [10135] 21. Gray, M. Violet; Greaves, James M. 1984. Riparian forest as habitat for the least Bell's vireo. 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: 605-611. [5862] 22. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 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. Hansen, Paul; Chadde, Steve; Pfister, Robert; [and others]. 1988. Riparian site types, habitat types, and community types of southwestern Montana. Missoula, MT: University of Montana, School of Forestry, Montana Riparian Association. 140 p. [5883] 25. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. [6851] 26. 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] 27. Hitchcock, C. Leo; Cronquist, Arthur. 1964. Vascular plants of the Pacific Northwest. Part 2: Salicaceae to Saxifragaceae. Seattle, WA: University of Washington Press. 597 p. [1166] 28. Hosner, John F.; Minckler, L. S. 1960. Hardwood reproduction in the river bottoms of southern Illinois. Forest Science. 6(1): 67-77. [3738] 29. Houston, Douglas B. 1968. The Shiras Moose in Jackson Hole, Wyoming. Tech. Bull. No. 1. [Place of publication unknown]: The Grand Teton Natural History Association. 110 p. [7824] 30. Irwin, Larry L. 1985. Foods of moose, Alces alces, and white-tailed deer, Odocoileus virginianus, on a burn in boreal forest. Canadian Field-Naturalist. 99(2): 240-245. [4513] 31. Komarkova, Vera; Alexander, Robert R.; Johnston, Barry C. 1988. Forest vegetation of the Gunnison and parts of the Uncompahgre National Forests: a preliminary habitat type classification. Gen. Tech. Rep. RM-163. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 65 p. [5798] 32. 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] 33. 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] 34. Lanner, Ronald M. 1983. Trees of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 215 p. [1401] 35. Lindauer, Ivo E. 1983. A comparison of the plant communities of the South Platte and Arkansas River drainages in eastern Colorado. Southwestern Naturalist. 28(3): 249-259. [5886] 36. Little, Elbert L., Jr. 1979. Checklist of United States trees (native and naturalized). Agric. Handb. 541. Washington, DC: U.S. Department of Agriculture, Forest Service. 375 p. [2952] 38. 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] 39. Medina, Alvin L. 1986. Riparian plant communities of the Fort Bayard watershed in southwestern New Mexico. Southwestern Naturalist. 31(3): 345-359. [1629] 40. Monsen, Stephen B. 1983. Plants for revegetation of riparian sites within the Intermountain region. In: Monsen, Stephen B.; Shaw, Nancy, compilers. 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Related categories for Species: Salix exigua | Sandbar Willow

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