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Introductory

SPECIES: Symphoricarpos occidentalis | Western Snowberry
ABBREVIATION : SYMOCC SYNONYMS : NO-ENTRY SCS PLANT CODE : SYOC COMMON NAMES : western snowberry wolfberry TAXONOMY : The currently accepted scientific name of western snowberry is Symphoricarpos occidentalis Hook. (Caprifoliaceae) [50,57,62,77]. There are no recognized infrataxa. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Lora L. Esser, August 1995 LAST REVISED BY AND DATE : AUTHORSHIP AND CITATION : Esser, Lora L. 1995. Symphoricarpos occidentalis. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Symphoricarpos occidentalis | Western Snowberry
GENERAL DISTRIBUTION : Western snowberry occurs from British Columbia east to Ontario and south to Washington, Utah, New Mexico, Oklahoma, and Missouri [50,114,127]. It is also found in Michigan [77,114,131]. Western snowberry is most commonly found in the northern Great Plains [50]. ECOSYSTEMS : FRES10 White-red-jack pine FRES11 Spruce-fir FRES17 Elm-ash-cottonwood FRES19 Aspen-birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir-spruce FRES25 Larch FRES28 Western hardwoods FRES29 Sagebrush FRES35 Pinyon-juniper FRES36 Mountain grasslands FRES37 Mountain meadows FRES38 Plains grasslands FRES39 Prairie STATES : CO ID IL IA KS MI MN MO MT NE NM ND OK SD UT WA WI WY AB BC MB ON SK ADMINISTRATIVE UNITS : BADL BICA BLCA DETO DINO FOUS GLAC KNRI PIPE ROMO SCBL WICA YELL BLM PHYSIOGRAPHIC REGIONS : 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 13 Rocky Mountain Piedmont 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K012 Douglas-fir forest K015 Western spruce-fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine-Douglas-fir forest K024 Juniper steppe woodland K037 Mountain-mahogany-oak scrub K038 Great Basin sagebrush K050 Fescue-wheatgrass K055 Sagebrush steppe K056 Wheatgrass-needlegrass shrubsteppe K063 Foothills prairie K064 Grama-needlegrass-wheatgrass K066 Wheatgrass-needlegrass K067 Wheatgrass-bluestem-needlegrass K068 Wheatgrass-grama-buffalograss K069 Bluestem-grama prairie K070 Sandsage-bluestem prairie K074 Bluestem prairie K075 Nebraska Sandhills prairie K081 Oak savanna K093 Great Lakes spruce-fir forest K095 Great Lakes pine forest K098 Northern floodplain forest K101 Elm-ash forest SAF COVER TYPES : 1 Jack pine 12 Black spruce 15 Red pine 16 Aspen 18 Paper birch 21 Eastern white pine 42 Bur oak 63 Cottonwood 210 Interior Douglas-fir 212 Western larch 213 Grand fir 215 Western white pine 217 Aspen 220 Rocky Mountain juniper 222 Black cottonwood-willow 224 Western hemlock 227 Western redcedar-western hemlock 228 Western redcedar 235 Cottonwood-willow 236 Bur oak 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : 102 Idaho fescue 109 Ponderosa pine shrubland 301 Bluebunch wheatgrass-blue grama 303 Bluebunch wheatgrass-western wheatgrass 304 Idaho fescue-bluebunch wheatgrass 309 Idaho fescue-western wheatgrass 310 Needle-and-thread-blue grama 311 Rough fescue-bluebunch wheatgrass 316 Big sagebrush-rough fescue 401 Basin big sagebrush 402 Mountain big sagebrush 409 Tall forb 411 Aspen woodland 413 Gambel oak 415 Curlleaf mountain-mahogany 416 True mountain-mahogany 421 Chokecherry-serviceberry-rose 422 Riparian 601 Bluestem prairie 602 Bluestem-prairie sandreed 603 Prairie sandreed-needlegrass 606 Wheatgrass-bluestem-needlegrass 607 Wheatgrass-needlegrass 608 Wheatgrass-grama-needlegrass 609 Wheatgrass-grama 613 Fescue grassland HABITAT TYPES AND PLANT COMMUNITIES : Western snowberry occurs in a variety of habitats including grassland, mixed-grass prairie, shrubland, sagebrush, woodland, and riparian [2,5,7,21,56,66]. Western snowberry is common in floodplain and riparian habitats. In Montana western snowberry is found along the floodplain of the Yellowstone River. Common associates include plains cottonwood (Populus deltoides var. monilifera), willows (Salix spp.), and Wood's rose (Rosa woodsii) [2,18]. In Wyoming and Colorado western snowberry is a common riverine floodplain shrub in plains cottonwood and willow communities [31,42,90,103]. Associates include peachleaf willow (Salix amygdaloides), thinleaf alder (Alnus incana ssp. tenuifolia), chokecherry (Prunus virginiana), and red-osier dogwood (Cornus sericea). In eastern Montana and western North and South Dakota, western snowberry is an important species in woodland and riparian draws dominated by green ash (Fraxinus pennsylvanica) [21,47]. A green ash/western snowberry habitat type has been described. Common associates include American elm (Ulmus americana), boxelder (Acer negundo), silver buffaloberry (Shepherdia argentea), Saskatoon serviceberry (Amelanchier alnifolia), American plum (Prunus americana), and chokecherry. In western Montana western snowberry may form dense ecotonal thickets around silver buffaloberry stands [54]. A western snowberry shrub community type has been described for Montana, North Dakota, and Alberta [5,54,55,56]. Western snowberry often forms dense monotypic stands with little understory. Some common understory species include rough fescue (Festuca scabrella), Kentucky bluegrass (Poa pratense), and western wheatgrass (Pascopyrum smithii). Western snowberry is an important species in native shortgrass and mixed-grass prairies of the northern Great Plains. In North Dakota western snowberry is commonly found in shrub-grassland communities dominated by western wheatgrass, needlegrass (Stipa spp.), blue grama (Bouteloua gracilis), and little bluestem (Schizachyrium scoparium) [7,23,28,82]. In the Black Hills a bur oak (Quercus macrocarpa)/western snowberry habitat type has been described. Associates include Oregon-grape (Mahonia repens), red raspberry (Rubus idaeus), American hazel (Corylus americana), and smooth sumac (Rhus glabra) [1,64]. Western snowberry is found in forested habitats dominated by Douglas-fir (Pseudotsuga menziesii) and ponderosa pine (Pinus ponderosa) [16,81]. In British Columbia a Douglas-fir/Idaho fescue (Festuca idahoensis)-western snowberry association is described [81]. In Alberta and Saskatchewan western snowberry is commonly found in quaking aspen (Populus tremuloides) parkland with rough fescue, porcupine grass (Stipa spartea), and silverberry (Elaeagnus commutata) [4,29]. The following publications list western snowberry as a community dominant: Classification and management of riparian and wetland sites in northwestern Montana [19] Native woodland habitat types of southwestern North Dakota [48] Classification and management of riparian-wetland shrub sites in Montana [53] The vegetation of the Grand River/Cedar River, Sioux, and Ashland Districts of the Custer National Forest: a habitat type classification [54] The vegetation of Theodore Roosevelt National Park, North Dakota: a habitat type classification [55] Forest vegetation of the Black Hills National Forest of South Dakota and Wyoming: a habitat type classification [64]

VALUE AND USE

SPECIES: Symphoricarpos occidentalis | Western Snowberry
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Western snowberry is a valuable forage species for mule deer, white-tailed deer, elk, and pronghorn [2,34,61,80,117]. It is browsed by white-tailed deer in Montana and constituted 60 percent of white-tailed deer early winter diets in 1965. Western snowberry was found in 95 percent of all rumens and averaged 27 percent of rumen volume year-round [2]. In North and South Dakota western snowberry is an important browse species in mule deer and pronghorn fall and winter diets [72,104,141]. In Saskatchewan western snowberry is browsed by pronghorn and constituted 17 percent of pronghorn diets from October 30 to November 3, 1960 [34]. In Montana, North Dakota, and South Dakota, western snowberry fruits are eaten by sharp-tailed grouse, passerine birds, and small mammals [35,39,96,114]. In the northern Great Plains, the fruit of western snowberry is an important fall and winter food for sharp-tailed grouse [39]. In Wyoming sharp-tailed grouse feed on western snowberry fruits [87]. In Alberta snowshoe hares browse western snowberry [93]. In Utah and Idaho western snowberry is important winter forage for cattle [94,112]. In North Dakota cattle make limited use of western snowberry [72]. In Nebraska western snowberry is poor forage for cattle and fair for sheep [117]. In Montana forage production under dense thickets of western snowberry is low; as stands open up, forage production increases due to invasion by Kentucky bluegrass [56]. PALATABILITY : Palatability ratings for western snowberry are as follows [19,35]: CO MT ND UT WY cattle fair fair fair poor fair sheep fair fair fair fair fair horses fair poor fair poor fair deer ---- good ---- ---- ---- elk ---- good ---- ---- ---- NUTRITIONAL VALUE : Western snowberry nutritional values are rated as follows [35]: UT CO WY MT ND elk good poor fair fair ---- mule deer good poor fair good fair white-tailed deer ---- ---- good good fair pronghorn ---- ---- fair fair fair upland game birds good ---- good fair fair waterfowl poor ---- poor ---- poor small nongame birds fair ---- good fair ---- small mammals good ---- good fair ---- Western snowberry energy rating and protein content are fair [19,35]. In Alberta percent digestible protein of dry matter at leaf stage, heading stage, and seed ripe stage was 4.0, 1.8, and 1.0, respectively [14]. In Saskatchewan crude protein content of western snowberry browse was 7.9 percent in February, 25.1 percent in May, 12.3 percent in June, 10.2 percent in July, and 15.2 percent in September [34]. COVER VALUE : Western snowberry cover values are rated as follows [19,35]: CO MT ND UT WY elk ---- poor fair ---- poor mule deer ---- fair good fair poor white-tailed deer poor good ---- ---- fair pronghorn ---- fair good ---- fair upland game birds ---- good good good good waterfowl ---- good fair poor poor small nongame birds ---- good good good good small mammals ---- good ---- good good Dense thickets of western snowberry provide important thermal and hiding cover for wildlife [56,114,130]. In South Dakota western snowberry provides cover for wild turkeys [102]. In the northern Great Plains, western snowberry provides nesting cover for sharp-tailed grouse, upland waterfowl, and many species of passerine birds [30,51,72,78]. In North Dakota 68 percent of mallard nests were on sites dominated by western snowberry [30]. VALUE FOR REHABILITATION OF DISTURBED SITES : Western snowberry adapts well to disturbed or degraded sites [95,114]. It is used for erosion control, wildlife habitat enhancement, and land reclamation [56,94,130]. Nursery-grown stock and rooted cuttings readily establish on disturbed sites and once established, western snowberry is a good soil stabilizer [19,56,95,114]. Western snowberry is recommended for planting in riparian areas [83,95]. In Colorado western snowberry is a high priority species for oil shale restoration [130]. OTHER USES AND VALUES : Plains Indians used western snowberry for food, implement-making, and eye disease treatment [94]. Western snowberry is planted as an ornamental [127]. MANAGEMENT CONSIDERATIONS : Western snowberry increases with heavy grazing pressure [7,51,69]. In North Dakota western snowberry was more abundant on grazed green ash sites than on adjacent ungrazed sites [47]. At the Central Grasslands Research Station in North Dakota, 5 years of cattle grazing under various management strategies and stocking rates did not consistently alter the structure or composition of western snowberry communities [72]. Land management practices that promote or maintain sizeable tracts of western snowberry will favor higher densities and species richness of passerines [7]. In South Dakota the preservation of western snowberry thickets will improve wild turkey nesting habitat [135]. Western snowberry is susceptible to insect parasites and root rot fungi [94]. According to Watson [131], western snowberry is susceptible to herbicide damage. Western snowberry is effectively controlled with multiple applications of dicamba plus 2,4-DE [22].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Symphoricarpos occidentalis | Western Snowberry
GENERAL BOTANICAL CHARACTERISTICS : Western snowberry is a native, deciduous, rhizomatous perennial shrub that forms dense colonies by adventitious shoots from widely spreading roots and rhizomes [19,50,56,77,130]. In Minnesota colonies from 3.3 to 660 feet (1-200 m) in diameter have been reported [94]. Western snowberry is an erect shrub that grows from 2 to 4 feet (0.6-1.2 m) tall [50,62,130]. Leaves are 0.8 to 2.4 inches (2-6 cm) long and 0.4 to 1.4 inches (1-3.5 cm) wide [50,117]. The berrylike drupe contains 2 nutlets and ripens in the fall [38,112,127]. In Minnesota roots of western snowberry penetrated to a depth of 5.2 feet (155 cm) in loamy sand and rhizomes to a depth of 1.2 feet (35 cm) [94]. A study in Minnesota showed that western snowberry stems ranged from 3 to 13 years old, with an average age of 7.2. Rhizomes ranged from 5 to 40 years old, with an average age of 18.9 [94]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Sexual: Western snowberry reproduces by seed [22,35,38]. Seed is pollinated by insects and dispersed by birds and mammals [38,94]. Seed may be stored in dry sealed containers at 41 degrees Fahrenheit (5 deg C) for up to 2 years with moderate loss of viability [127]. The seed is surrounded by a stony endocarp which may offer some resistance to germination. Western snowberry has embryo dormancy; an afterripening period is necessary for adequate germination. Warm stratification at room temperature for 3 to 4 months followed by cold stratification at 41 degrees Fahrenheit (5 deg C) for 4 to 6 months increases germination [38,94,127]. In the laboratory a constant temperature of 50 degrees Fahrenheit (10 deg C) produces a germination rate of 44.1 percent [94]. Vegetative: Western snowberry reproduces vegetatively by root sprouts and rhizomes [22,68,94]. According to Pelton [94], shoots from rhizomes are more common than seedlings. Adventitious shoots develop in the spring and by the end of the first year they reach mature stem height [94]. SITE CHARACTERISTICS : Western snowberry is commonly found in riparian areas such as alluvial floodplain terraces, upland ravines, swale-like depressions, and along streams and rivers [48,54,56,57,130]. It is also common in open deciduous woods, open prairies, rocky bluffs, pastures, and along roadsides [50,62,94,114,127]. Western snowberry grows best on moist soils with good drainage [18,34,62,112]. It will grow in semishaded areas and on dry, exposed hillsides [54,114,127]. It grows best on loam and sandy loam soils, but occurs on clay, clay loam, and gravelly substrates as well [18,35,50,94,131]. Western snowberry is tolerant of poorly drained soils and some flooding, but is intolerant of prolonged flooding and permanently high water tables [54,56]. Elevations for western snowberry are as follows: feet meters Colorado 3,500-8,500 1,050-2,550 [35,57] Montana 1,950-4,000 594-1,200 [56] North Dakota 800-1,800 240-540 [140] South Dakota 4,125-7,000 1,250-2,100 [17,92] Utah 5,030-6,270 1,525-1,900 [34,134] Wyoming 7,525-9,900 2,280-3,000 [42] Alberta 2,000-4,685 610-1,420 [4,137] SUCCESSIONAL STATUS : Western snowberry is a generally shade intolerant species of sparse woods, riparian sites, and open areas where there is often evidence of past disturbance [15,40,79,130,131]. Western snowberry is a pioneer species following broadcast burning and cattle grazing [8,56,130,131]. In the northern Great Plains western snowberry invades grasslands [29,58,133]; it also occurs on stable portions of streambanks [20]. Western snowberry is a highly competitive species but can be suppressed by taller woody plants such as green ash [20,56,130]. In the northern Great Plains, western snowberry forms dense, nearly impenetrable thickets, often excluding other vegetation [20,56,94,130]. In Minnesota colonies of western snowberry range in size from 3.3 to 6.6 feet (1-2 m) to 165 to 247 feet (50-75 m) in diameter [94]. SEASONAL DEVELOPMENT : Western snowberry flowering dates are as follows: Colorado Jun-Aug [35] Great Plains Jun-Aug [50,114] Illinois Jun-Aug [49] Montana June [35] New Mexico May-July [127] North Dakota Jun-July [27,35] Oklahoma May-July [127] South Dakota Jun-July [39] Wyoming July [35] Fruit ripening occurs from August to September in the southwestern states, and from September to October in the northern Great Plains [114,127]. Seed dispersal occurs from September into early winter [116].

FIRE ECOLOGY

SPECIES: Symphoricarpos occidentalis | Western Snowberry
FIRE ECOLOGY OR ADAPTATIONS : Western snowberry sprouts vigorously from the root crown and rhizomes following fire [6,47,56,100,105]; stands are usually denser in burned than in adjacent unburned areas [56]. Spring and fall fires induce western snowberry sprouting, but frequent fires may reduce cover [59]. Western snowberry probably establishes from off-site seed dispersed by birds and mammals. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown Rhizomatous shrub, rhizome in soil Ground residual colonizer (on-site, initial community) Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Symphoricarpos occidentalis | Western Snowberry
IMMEDIATE FIRE EFFECT ON PLANT : Western snowberry is top-killed or killed by severe fires [4,5,60,94]. In the northern Great Plains, "hot" fires in late summer and early fall have severely burned roots of western snowberry [60]. In Minnesota in a partially burned colony of western snowberry, all stems were killed and all stem bases charred. By the fall of the same year, an average of 2.5 sprouts per stem base was observed [94]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Western snowberry sprouts from the root crown following fire [100]. Several studies have reported rapid recovery and postfire increases in western snowberry densities [5,11,43,100], although decreases have been reported [3,4,11,45]. In quaking aspen parklands in Alberta, western snowberry sprouted 2 weeks after spring fire; by 3 months its canopy cover was greater on burned sites than on control plots [5]. In Saskatchewan a prescribed fire occurred in October 1976 in native fescue grassland; western snowberry was top-killed. By postfire year 1, western snowberry live stem density was similar in burned and unburned areas [97]. In North Dakota an October 1976 fire burned mixed-grass prairie and wooded draw plant communities. Average densities (stems/sq m) of western snowberry in the summers of 1977 and 1978 were higher on burned than unburned transects in wooded draws [142]: 1977 1978 lower draw-burned 41.2 31.5 upper draw-burned 68.6 38.8 unburned ---- 12.5 In Saskatchewan eight prescribed fires were set from October 1986 to April 1988 to reduce western snowberry encroachment into native grassland. Two plots were burned with headfires at each of the following times: mid-October 1986, mid-October 1987, early May 1987, and late April 1988; two additional blocks were left as control sites. All plots were monitored for 4 years after burning. Average western snowberry stem densities (stems/sq m) were higher on burned than unburned plots [100]: growing season control autumn spring standard error prefire 36 39 38 8.1 postfire year 1 39a* 72ab 122b 14.6 postfire year 2 43a 67ab 111b 12.3 postfire year 3 46 62 95 12.9 postfire year 4 46 57 51 5.5 *Different letters within a year indicate means are significantly different (P< or =0.05). A similar letter or no letter within a year indicates means are not significantly different (P> or =0.05) Western snowberry density was significantly greater on spring-burned plots than on autumn-burned or control plots. In Alberta two prescribed burns were conducted on May 8, 1970 and May 11, 1971. Western snowberry was the dominant shrub on unburned sites. All western snowberry stems were killed by the fires, but plants started sprouting 2 weeks after fire. Stem densities (stems/sq m) for western snowberry during three growing seasons following spring 1970 burning were as follows [5]: year unburned burned 1970 86 236 1971 65 199 1972 66 170 Western snowberry stem densities increased significantly (P<0.05) following fire. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : In South Dakota a May 1, 1974 prescribed fire was conducted in native grassland. Stem density (stems/sq m) and average height (cm) of western snowberry were reduced following fire. Results were as follows [45]: prefire postfire (Ocotber 15, 1973) (June 28, 1974) stem density 79 55 stem height 61 24 In Alberta early spring burning in fescue grassland was conducted annually for 24 years. Stem densities (stem/sq m) were 17.8 and 25 in burned and unburned areas, respectively. Frequency and cover of western snowberry in July 1976 after the last fire were as follows [3,4]: frequency (%) cover (%) unburned 56 31 burned 52 2 Western snowberry canopy cover declined greatly on burned sites, but frequency and stem density did not change significantly. In Minnesota prescribed spring fires were conducted annually from 1983 to 1987. Western snowberry shoot height decreased from 3.3 to 1.6 feet (1-0.5 m) on burned sites [11]. FIRE MANAGEMENT CONSIDERATIONS : In the absence of fire, western snowberry has become the dominant native shrub on mixed-grass prairies in the northern Great Plains [111]. Annual burning may restrict expansion of western snowberry colonies onto native prairie grasslands, whereas periodic burning may enhance the spread of western snowberry [5,60,94,100]. Periodic burning could create even-aged, youthful stands of western snowberry, which may be more productive of wildlife forage and provide better cover [100]. In North Dakota two prescribed fires in mid-June 1982 and 1984 top-killed most western snowberry. Unburned vegetation ("skips") within burn areas mostly occurred in dense patches of western snowberry. Gadwalls started nesting in these "skips" 4 days after the burns, where dead stems of western snowberry were still standing [75].

REFERENCES

SPECIES: Symphoricarpos occidentalis | Western Snowberry
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Canadian Journal of Botany. 57: 2820-2823. [2867] 6. Archibold, O. W. 1979. Buried viable propagules as a factor in postfire regeneration in northern Saskatchewan. Canadian Journal of Botany. 57: 54-58. [5934] 7. Arnold, Todd W.; Higgins, Kenneth F. 1986. Effects of shrub coverages on birds of North Dakota mixed-grass prairies. Canadian Field-Naturalist. 100(1): 10-14. [23671] 8. Bailey, A. W.; Irving, B. D.; Fitzgerald, R. D. 1990. Regeneration of woody species following burning and grazing in aspen parkland. Journal of Range Management. 43(3): 212-215. [11775] 9. Bailey, Arthur W.; Anderson, Murray L. 1980. Fire temperatures in grass, shrub and aspen forest communities of central Alberta. Journal of Range Management. 33(1): 37-40. [6937] 10. Bayless, Steve. 1971. Relationships between big game and sagebrush. Paper presented at: Annual meeting of the Northwest Section of the Wildlife Society; 1971 March 25-26; Bozeman, MT. 14 p. On file with: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. [17098] 11. Becker, Donald A. 1989. Five years of annual prairie burns. In: Bragg, Thomas A.; Stubbendieck, James, eds. Prairie pioneers: ecology, history and culture: Proceedings, 11th North American prairie conference; 1988 August 7-11; Lincoln, NE. Lincoln, NE: University of Nebraska: 163-168. [14037] 12. Benninger-Truax, Mary; Vankat, John L.; Schaefer, Robert L. 1992. Trail corridors as habitat and conduits for movement of plant species in Rocky Mountain National Park, Colorado, USA. Landscape Ecology. 6(4): 269-278. [22175] 13. 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] 14. Bezeau, L. M.; Johnston, A. 1962. In vitro digestibility of range forage plants of the Festuca scabrella association. Canadian Journal of Plant Science. 42: 692-697. [441] 15. Bird, Ralph D. 1930. Biotic communities of the aspen parkland of central Canada. Ecology. 11(2): 356-442. [15277] 16. Bock, Carl E.; Bock, Jane H. 1983. Responses of birds and deer mice to prescribed burning in ponderosa pine. Journal of Wildlife Management. 47(3): 836-840. [476] 17. Bock, Jane H.; Bock, Carl E. 1984. Effects of fires on woody vegetation in the pine-grassland ecotone of the southern Black Hills. American Midland Naturalist. 112(1): 35-42. [477] 18. Boggs, Keith Webster. 1984. Succession in riparian communities of the lower Yellowstone River, Montana. Bozeman, MT: Montana State University. 107 p. Thesis. [7245] 19. 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] 20. Boggs, Keith; Weaver, T. 1992. Response of riparian shrubs to declining water availability. 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: 48-51. [19094] 21. Boldt, Charles E.; Uresk, Daniel W.; Severson, Kieth E. 1979. Riparian woodlands in jeopardy on Northern High Plains. In: Johnson, R. Roy; McCormick, J. Frank, technical coordinators. Strategies for protection & 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: 184-189. [4359] 22. Bowes, G. G. 1991. Long-term control of aspen poplar and western snowberry with dicamba and 2,4-D. Canadian Journal of Plant Science. 71(4): 1121-1131. [19502] 23. Brand, M. D.; Goetz, H. 1978. Secondary succession of a mixed grass community in southwestern North Dakota. Annual Proceedings of the North Dakota Academy of Science. 32(2): 67-78. [7512] 24. Britton, Carlton M.; Wright, Henry A. 1983. Brush management with fire. In: McDaniel, Kirk C., ed. Proceedings--brush management symposium; 1983 February 16; Albuquerque, NM. Denver, CO: Society for Range Management: 61-68. [521] 25. Bromley, Peter T. 1977. Aspects of the behavioural ecology and sociobiology of the pronghorn (Antilocapra americana). Calgary, AB: University of Calgary. 370 p. Dissertation. [8088] 26. Buell, Murray F.; Facey, Vera. 1960. Forest-prairie transition west of Itasca Park, Minnesota. 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