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Introductory

WILDLIFE SPECIES: Centrocercus urophasianus | Sage Grouse
ABBREVIATION : CEUR COMMON NAMES : sage grouse sage hen sage chicken TAXONOMY : The currently accepted scientific name of sage grouse is Centrocercus urophasianus (Bonaparte). There are two recognized subspecies: the eastern sage grouse, C. u. ssp. urophasianus, and the western sage grouse, C. u. ssp. phaios Aldrich [1]. Sage grouse is a member of the family Phasianidae [37]. Sage grouse hybridizes rarely with sharp-tailed grouse (Tympanuchus phasianellus) and blue grouse (Dendragapus obscurus) [28]. ORDER : Galliformes CLASS : Bird FEDERAL LEGAL STATUS : No special status OTHER STATUS : Sage grouse is noted on the Audubon Society's Blue List as a species of special concern in Oregon, Washington, and adjacent Canada [50]. The California Department of Fish and Game lists it as a species of special concern [10]. COMPILED BY AND DATE : C. L. Bushey, June 1986 LAST REVISED BY AND DATE : Janet L. Howard, March 1996 AUTHORSHIP AND CITATION : Howard, Janet L. 1996; Bushey, C. L. 1986. Centrocercus urophasianus. In: Remainder of Citation

WILDLIFE DISTRIBUTION AND OCCURRENCE

WILDLIFE SPECIES: Centrocercus urophasianus | Sage Grouse
GENERAL DISTRIBUTION : Sage grouse are distributed from north-central Oregon, southern Idaho, and southern Alberta and Saskatchewan south to eastern California, western Colorado, and extreme western North and South Dakota. Isolated populations occur in New Mexico, where sage grouse were extirpated but have been reintroduced, and in eastern Washington [28,37,54]. Sage grouse have been extirpated in British Columbia, most of North and South Dakota, Nebraska, Kansas, Oklahoma, Arizona (except the extreme northwestern tip), and central California [23,26,37]. Western sage grouse occurs only in eastern Washington and Oregon. The ranges of western and eastern sage grouse overlap in Oregon. Eastern sage grouse occur in all states and provinces within the range of sage grouse except Washington [1,12]. ECOSYSTEMS : FRES29 Sagebrush STATES :
AZ CA CO ID MT NV NM ND OR SD UT WA WY
AB SK
BLM PHYSIOGRAPHIC REGIONS : 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 7 Lower Basin and Range 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 13 Rocky Mountain Piedmont 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K024 Juniper steppe woodland K038 Great Basin sagebrush K055 Sagebrush steppe K056 Wheatgrass-needlegrass shrubsteppe SAF COVER TYPES : NO-ENTRY SRM (RANGELAND) COVER TYPES : 107 Western juniper/big sagebrush/bluebunch wheatgrass 314 Big sagebrush-bluebunch wheatgrass 315 Big sagebrush-Idaho fescue 316 Big sagebrush-rough fescue 320 Black sagebrush-bluebunch wheatgrass 321 Black sagebrush-Idaho fescue 324 Threetip sagebrush-Idaho fescue 405 Black sagebrush 406 Low sagebrush 407 Stiff sagebrush 408 Other sagebrush types 612 Sagebrush-grass PLANT COMMUNITIES : Sage grouse are obligate residents of the sagebrush (Artemisia spp.) ecosystem, usually inhabiting sagebrush-grassland or juniper (Juniperus spp.)-sagebrush-grassland communities. Meadows surrounded by sagebrush may be used as feeding grounds [27]. Sage grouse occur throughout the range of big sagebrush (A. tridentata), except on the periphery of big sagebrush distribution or in areas where it has been eliminated [12]. Sage grouse prefer mountain big sagebrush (A. t. ssp. vaseyana) and Wyoming big sagebrush (A. t. ssp. wyomingensis) communities to basin big sagebrush (A. t. spp. tridentata) communities. Sagebrush cover types other than big sagebrush can fulfill sage grouse habitat requirements; in fact, sage grouse may prefer other sagebrush cover types to big sagebrush. Sage grouse in Antelope Valley, California, for example, use black sagebrush (A. nova) cover types more often than the more common big sagebrush cover types [45]. Sagebrush communites not included in SRM cover types but supporting sage grouse include silver sagebrush (A. cana) and fringed sagebrush (A. frigida) [41,55]. Sage grouse use of less common sagebrush communities (i.e., Bigelow sagebrush [A. bigelovii]) may occur but is not documented in current literature. REFERENCES : NO-ENTRY

BIOLOGICAL DATA AND HABITAT REQUIREMENTS

WILDLIFE SPECIES: Centrocercus urophasianus | Sage Grouse
TIMING OF MAJOR LIFE HISTORY EVENTS : Courtship/nesting - Males gather on the lek in late February to April, as soon as the lek is relatively free of snow. Only a few dominant males, usually two, breed. Sage grouse mating behaviors, which are complex, are summarized by Johnsgard [27]. After mating, the hen leaves the lek for the nesting grounds. Clutch size ranges from six to eight eggs; incubation time is 25 to 27 days. Sage grouse apparently have high rates of nest desertion and nest predation [21,27]. Summarizing data from several sage grouse studies, Gill [20] found a range of nesting success from 23.7 to 60.3 percent, with predation accounting for 26 to 76 percent of lost nests. Brooding - Chicks fly by 2 weeks of age, although their movements are limited until they are 2 to 3 weeks old [54]. They can sustain flight by 5 to 6 weeks of age. Juveniles are relatively independent by the time they have compeleted their first molt at 10 to 12 weeks of age [28]. Seasonal movements - Fall movements to wintering areas are driven by weather conditions and usually occur gradually. After late winter or spring lekking activity, sage grouse may move to higher elevations or down to irrigated valleys for nesting and feeding. Brooding ranges may be a considerable distance from winter ranges or spring nesting grounds. Schlatterer [46] reported that in southern Idaho, brooding grounds were 13 to 27 miles (21-43 km) from the nesting grounds. Males may also move long distances over the seasons. During winter in Wyoming, Patterson [38] recovered a male sage grouse 75 air miles (120 km) from where he had banded it the previous summer. PREFERRED HABITAT : Sage grouse are totally dependent on sagebrush-dominanted habitats [5]. Sagebrush is a crucial component of their diet year-round, and sage grouse select sagebrush almost exclusively for cover [38]. Because sage grouse habitat and cover requirements are inseparably tied to sagebrush, they will be discussed together. Winter - The best winter habitat is below snowline, where sagebrush is available all winter [44]. Dalke and others [13] reported that wintering grounds of sage grouse in Idaho were usually where snow accumulation was less than 6 inches (15 cm). In areas of deep snow, sage grouse winter where sagebrush has grown above the snow level [2]. In winter and throughout the year, sage grouse select areas of little or no slope. In a Colorado study, nearly 80 percent of sage grouse winter use of 500 square miles (1,252 sq km) of sagebrush was on less than 35 square miles (87 sq km): on flat areas where sagebrush projected above the snow, or on south- or west-facing sites of less than 5 percent slope, where sagebrush was sometimes quite short but still accessible [28]. In Montana prime wintering areas were flat, large expanses of dense sagebrush; winter home ranges of five females in Montana varied from 2,615 to 7,760 acres (1,050-3,100 ha) during 2 different years [16]. Lekking grounds - Open areas such as swales, irrigated fields, meadows, burns, and roadsides and areas with low, sparse sagebrush cover are used as leks [31]. Of 45 leks, Patterson [38] reported that 11 were on windswept ridges or exposed knolls, 10 were in flat sagebrush, 7 were in bare openings, and the remaining 17 were on various other site types. Leks are usually surrounded by areas with 20 to 50 percent sagebrush cover, with sagebrush no more than 1 foot (30.5 cm) tall. When not on the lek, sage grouse disperse to the surrounding areas [54]. Some females probably travel between leks. In Mono County, California, the home range of marked females during 1 month of the breeding season was 750 to 875 acres (300 to 350 ha), enough area to include several active leks [9]. Nesting - Sage grouse prefer relatively tall sagebrush with an open canopy for nesting. Hens usually nest near the lekking grounds [46], but some hens have been noted to fly as far as 12 to 20 miles (19-32 km) to favorable nesting sites [20,44]. In Utah, 33 percent of 161 nests were under silver sagebrush (Artemisia cana) that was 14 to 25 inches (36-63.5 cm) tall, while big sagebrush of the same height accounted for 24 percent of nests [41]. In a threetip sagebrush (A. tripartata) habitat averaging 8 inches (20 cm) in height, hens selected the tallest plants for nesting cover. No nests occurred where threetip sagebrush cover exceeded 35 percent. Similarly, Patterson [38] reported that in Wyoming, 92 percent of sage grouse nests in Wyoming big sagebrush were in areas where vegetation was 10 to 20 inches (25-51 cm) tall and cover did not exceed 50 percent. In Idaho no hens nested in areas with less than 10 percent sagebrush cover or where sagebrush cover was greater than 25 percent [31]. During the nesting season, cocks and hens without nests use relatively open areas for feeding, and roost in dense patches of sagebrush [30,31]. Brooding - Sage grouse brood in open sagebrush with a forb component. As the season progresses, they move to areas still containing green vegetation; by August, they are often clustered near permanent watering sites [30]. In 158 Montana locations, young brood used areas of low plant height (9 to 15 inches [23-38 cm]) and density, while older broods and adults used areas where plants were taller (7 to 25 inches [18-63.5 cm]) [35]. During summer and early fall, male sage grouse remain segregated from brood and hen flocks, typically remaining with 2 to 3 miles (3.2-4.8 km) of the lek [54]. COVER REQUIREMENTS : See PREFERRED HABITAT. FOOD HABITS : The importance of sagebrush in the diet of adult sage grouse is impossible to overestimate. Numerous studies have documented its year-round use by sage grouse [4,11,12,31,38,45,48,54,55]. A Montana study, based on 299 crop samples, showed that 62 percent of total food volume of the year was sagebrush. Between December and February it was the only food item found in all crops. Only between June and September did sagebrush constitute less than 60 percent of the sage grouse diet [54]. Sage grouse select sagebrush species differentially. Sage grouse in Antelope Valley, California, browsed black sagebrush more frequently than the more common big sagebrush [45]. Among the big sagebrush subspecies, basin big sagebrush is less nutritious and higher in terpenes than either mountain or Wyoming big sagebrush. Sage grouse prefer the other two subspecies to basin big sagebrush [2]. Sage grouse lack a muscular gizzard and cannot grind and digest seeds: They must consume soft-tissue foods [54]. Apart from sagebrush, the adult sage grouse diet consists largely of herbaceous leaves, which are utilized primarily in late spring and summer [15]. Sage grouse are highly selective grazers, choosing only a few plant genera. Dandelion (Taraxacum spp.), legumes (Fabaceae), yarrow (Achillea spp.) and wild lettuce (Lactuca spp.) account for most of their forb intake [2,48]. Martin [35] found that from July to September, dandelion comprised 45 percent of sage grouse intake; sagebrush comprised 34 percent. Collectively, dandelion, sagebrush, and two legume genera (Trifolium and Astragalus) contributed more than 90 percent of the sage grouse diet. Insects are a minor diet item for adult sage grouse. Martin, Zim, and Nelson [34] reported that insects comprised 2 percent of the adult sage grouse diet in spring and fall and 9 percent in summer. Sagebrush made up 71 percent of the year-round diet. In their first week of life, sage grouse chicks consume primarily insects, especially ants and beetles [38]. Their diet then switches to forbs, with sagebrush gradually assuming primary importance. In a Utah study, forbs composed 54 to 60 percent of the summer diet of juvenile sage grouse, while the diet of adult birds was 39 to 47 percent forbs [51]. Water: Sage grouse apparently do not require open water for day to day survival if succulent vegetation is available. They utilize free water if it is available, however. Sage grouse distribution is apparently seasonally limited by water in some areas. In summer, sage grouse in desert regions occur only near streams, springs, and water holes. In winter in Eden Valley, Wyoming, sage grouse have been observed regularly visiting partially frozen streams to drink from holes in the ice [11]. PREDATORS : Lack of recruitment has been noted in some sage grouse populations, and predation of juvenile sage grouse has been cited as a factor in sage grouse population decline. Lack of adequate nesting and brooding cover may account for high juvenile losses in many regions [29]. A decline in preferred prey may also result in increased predation on sage grouse. Kindschy [29] suggested that in southeastern Oregon, a decline in black-tailed jackrabbit (Lepus californicus) numbers may have caused predators to switch to sage grouse as their primary prey. Predator species: Coyote (Canis latrans) [29], bobcat (Lynx rufus) [3,29], badger (Taxidea taxus)[29], falcons (Falconidae) [39], and hawks, kites, and eagles (Accipitridae) [4,14,29,40] prey on adult and juvenile sage grouse. Crows and ravens (Corvus spp.) and magpies (Pica spp.) consume juvenile birds [29]. Coyote, ground squirrels (Spermophilus spp.), and badger are the most important mammalian nest predators. Among bird species, magpies and ravens commonly prey on sage grouse nests [28,25,54]. Sage grouse are a popular game bird. Sage grouse hunting is closely regulated in those states where it is allowed, and is not generally cited as a factor in sage grouse decline [2,8,27,28]. MANAGEMENT CONSIDERATIONS : Sage grouse once occurred virtually everywhere there was sagebrush. They have declined primarily because of loss of habitat due to overgrazing, elimination of sagebrush, and land development [23]. Sage grouse populations began declining from 1900 to 1915, when livestock utilization of sagebrush rangeland was heavy [38]. In the 50's and 60's, land agencies adopted a policy of aggressive sagebrush control in order to convert sagebrush types to grassland. Chaining, frequent fire, and herbicide treatments reduced sagebrush by several million acres and sage grouse numbers plummeted drastically [11,59]. Conversion of sagebrush types to grassland has since been brought into question as a management practice for both wildlife and livestock [27,28,45,54]. Call [11] stated that: "Any land use practice which has as its objective the permanent elimination of sagebrush and establishment of grasses in the Mountain West will ultimately reduce the collective carrying capacity of that range for livestock, elk, mule deer, antelope, sage grouse, and many smaller species of wildlife." Sage grouse have one of the lowest recruitment rates of any upland game bird in North America. Loss of habitat, predation, drought, and poor weather conditions during hatching and brooding periods have been cited as factors leading to poor recruitment [59]. Autenrieth and others [2], Braun, Britt, and Wallestad [58], Call [11], and Dalke and others [13] provide guidelines for management of sage grouse and their habitat. Sage grouse have used areas planted to crested wheatgrass (Agropyron cristatum) as lekking grounds. Given the ability of crested wheatgrass to replace sagebrush and forbs, however, crested wheatgrass plantings are not recommended in sage grouse habitat [4]. REFERENCES : NO-ENTRY

FIRE EFFECTS AND USE

WILDLIFE SPECIES: Centrocercus urophasianus | Sage Grouse
DIRECT FIRE EFFECTS ON ANIMALS : Fire-related mortality of sage grouse has not been documented in the literature. HABITAT RELATED FIRE EFFECTS : Depending on prefire habitat quality and the type of fire, fire can be beneficial or harmful to sage grouse. Sage grouse use sagebrush of different age classes and stand structures as lekking, nesting, brooding, and wintering grounds. Neither expansive dense sagebrush nor expansive open areas constitute optimal sage grouse habitat: Klebenow [31] reported that in three summers of sampling, no sage grouse were observed in large acreage, dense sagebrush in southern Idaho. Fire that creates a mosaic of sagebrush of different ages and structures would benefit sage grouse [31]. Newly burned areas interspersed with patches of sagebrush offer increased forb production while providing nesting and brooding cover [7,24,33,36]. The younger age classes of sagebrush that establish after fire offer more nutritious and palatable browse than do old sagebrush stands [19]. Additionally, burns provide new lekking sites: Sage grouse have established leks on burns in areas where open cover was lacking before fire. Sage grouse show lek fidelity, however, and may not use burns as lekking grounds if there is a sufficient number of old leks [5]. Fire always removes a certain amount of sage grouse food and cover. Griner [22] noted that burning resulted in a decline in sage grouse in Utah. If the burn is small in relationship to surrounding area, it will probably enhance sage grouse habitat. Fire that destroys large tracts of sagebrush, or destroys key winter habitat, can be harmful [30,31]. However, large-acreage fires do not always harm sage grouse. A 17,250-acre (6,900-ha) wildfire in mountain big sagebrush in southern Idaho burned in a mosaic pattern, leaving many unburned islands. The wildfire occurred at an ebb in the sage grouse population, so nesting sites were not limiting in the first postfire nesting season. Overall effect of the wildfire on the sage grouse population was apparently neutral: The sage grouse population increased after the fire, but this was part of a regional trend of sage grouse increase following several years of low reproduction. Martin [36] suggested that had nesting habitat been limiting, the large-acreage fire probably would have adversely affected the sage grouse population. FIRE USE : A diversity of sagebrush habitat, in terms of sage grouse food and cover, should be the management objective. Klebenow [31] recommends burning sagebrush on a rotational basis to create sage grouse habitat. Different patches should be burned each year or every few years, with as long as 20 years between burning each patch. Benson and others [5] recommend burning in patches of less than 100 acres in size. Because livestock may concentrate in small burns, livestock should be excluded from the burns for 2 to 3 years after fire to optimize revegetation. Lek/nesting grounds - Fire that occurs outside the mating season will probably not affect postfire sage grouse use of the grounds for mating. Fall wildfires on sage grouse leks in southern Idaho had no effect on sage grouse use of the leks the next breeding season [36]. Areas immediately surrounding leks, however, are heavily used as nesting grounds, and fire in areas surrounding leks may have a negative impact on consequent use of the surrounding areas by hens. Wallstad and Pyrah [56] recommend that sagebrush within 1.9 miles (3.2 km) of a lek not be burned in order to protect nesting habitat. This recommendation may be most applicable to areas where nesting habitat is limited, however. Gates and Eng [19] noted that on their southern Idaho study site, which was surrounded by 120 square miles (300 sq km) of Wyoming big sagebrush, nesting habitat was plentiful. While their summer-fall prescribed fires did burn near several established leks, the fires also created an open area that sage grouse used as a lekking ground the next spring. The fire treatment apparently did not deter hens from using grounds adjacent to the burns for nesting and brooding. Most radio-collared sage grouse hens nested within 3 miles (5 km) of the lek on which they were captured the year before fire treatment. The summer of postfire year 1, 5 of 11 collared hens moved their brood into agricultural areas adjacent to the burn. Broods apparently made little use of the burns as foraging areas. Schlatterer [46] and Dalke and others [13] noted that following unintentional fire, sage grouse used small burned openings as leks. To create openings in homogeneous sagebrush, Klebenow [31] recommended small fires, 1 to 10 acres (0.4-4 ha) in size. Spring fire is not recommended on sage grouse nesting grounds [2,33]. Fire on the nesting grounds is not recommended in any season if nesting habitat is limited [2]. Brooding: Fall spot fires burning several patches of a few acres can result in suitable brood rearing areas by increasing forb availability. Spot burns along edges of meadows where sagebrush is encroaching may also enchance brood rearing areas. Enough sagebrush-meadow ecotone must be left, however, to provide cover [2]. Martin [36] noted that in southern Idaho, broods neither preferred nor avoided large burned areas (P<0.05). Winter: Klebenow [31] does not recommend burning in winter habitat. Autenreith and others [2] recommend that fire in winter use areas be applied cautiously: What may appear as an excess of sagebrush in summer may provide only mimimal amounts of sagebrush in winter. They recommend that prior to burning, winter sage grouse distribution during peak snow conditions should be assessed so that key wintering grounds are not depleted by fire. Examples of Fire Use: Prescribed and wildfires in north-central Colorado had no significant effect (P>0.10) on sage grouse populations. The prescribed Deer Creek Fire was conducted in October 1987 and was 180 feet (60 m) east of a lek. It burned only 95 acres (38 ha) due to poor ignition conditions. Two wildfires occurred in the study area in August 1987. The Perdiz Wildfire burned 300 acres (120 ha), consuming 99 percent of sagebrush cover. The Thornburg Well Wildfire burned 3,000 acres (1,200 ha), removed "most" shrub cover, and burned within 2 miles (0.8 km) of a lek. Pre- and postfire counts of male sage grouse were as follows [5]: High counts of male sage grouse on leks, 1973-1990 -------------------------------------------------- Year Deer Creek Perdiz Thornburg Well Prescribed Fire Wildfire Wildfire -------------------------------------------------- 1973 37 1974 11 1975 27 1976 36 1977 31 36(b) 1978 41 32 1979 43 16(b) 35 1980 28 8 28 1981 52 3 20 1982 66 27 8(c) 1983 47 21 8(c) 1984 14 8 NC 1985 45 10 5(c) 1986 21 6 15(c) 1987 23 16 17(c) 1988 18(a) 17(a) 20(a) 1989 13 8 16 1990 21 21 16 ---------------------------------------------------- (a) First postfire count (b) Year of initial location (c) No systematic counts NC = no count The authors noted that the relationship between sage grouse population size and habitat alteration by the Colorado fires was difficult to assess [5]. Sage grouse poulation size may be cyclic [43]; winter severity is also suspected to affect population size [57]. Habitat alterations other than fire may have played a factor in postfire sage grouse population size. In this case, decreased mining activity on the Perdiz site in 1989 to 1990 may at least partially explain sage grouse population increase at that time [5]. Sage grouse summer foraging in a meadow on the Inyo National Forest, California, increased following prescribed fire. The fire was conducted in the fall of 1981 to remove Wyoming big sagebrush from the meadow and to increase the component of early seral grasses and forbs. Snowpack was 220 percent above normal in the first postfire winter, and cover of early seral herbaceous species increased "substantially" in the first postfire summer [24]. REFERENCES : NO-ENTRY

REFERENCES

WILDLIFE SPECIES: Centrocercus urophasianus | Sage Grouse
REFERENCES : 1. American Ornithologists' Union. 1983. Checklist of North American birds. 6th ed. Lawrence, KS: Allen Press, Inc. 877 p. [21234] 2. Autenrieth, Robert; Molini, William; Braun, Clait, eds. 1982. Sage grouse management practices. Tech. Bull No. 1. Twin Falls, ID: Western States Sage Grouse Committee. 42 p. [7531] 3. Bailey, Theodore N. 1981. Den ecology, population parameters and diet of eastern Idaho bobcats. In: Blum, L. G.; Escherich, P. C., eds. Bobcat research conference: Proceedings; 1979 October 16-18; Front Royal, VA. NWF Science and Technical Series No. 6. Washington, DC: National Wildlife Federation: 62-69. [24985] 4. Beck, D. I. 1975. Attributes of a wintering population of sage grouse, North Park, Colorado. Fort Collins, CO: Colorado State University. 49 p. Thesis. [5757] 5. Benson, Lee A.; Braun, Clait E.; Leininger, Wayne C. 1991. Sage grouse response to burning in the big sagebrush type. In: Comer, Robert D.; Davis, Peter R.; Foster, Susan Q.; [and others], eds. Issues and technology in the management of impacted wildlife: Proceedings of a national symposium; 1991 April 8-10; Snowmass Resort, CO. Boulder, CO: Thorne Ecological Institute: 97-104. [21766] 6. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434] 7. Blaisdell, James P. 1953. Ecological effects of planned burning of sagebrush-grass range on the upper Snake River Plains. Tech. Bull. 1975. Washington, DC: U.S. Department of Agriculture. 39 p. [462] 8. Blaisdell, James P.; Murray, Robert B.; McArthur, E. Durant. 1982. Managing Intermountain rangelands--sagebrush-grass ranges. Gen. Tech. Rep. INT-134. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 41 p. [467] 9. Bradbury, J. W.; Gibson, R. M.; McCarthy, C. E.; Vehrencamp, S. L. 1989. Dispersion of displaying male sage grouse. II. The role of female dispersion. Behavioral Ecology and Sociobiology. 24: 15-24. [25627] 10. California Department of Fish and Game, Natural Diversity Data Base. 1992. Special animals. Sacramento, CA: California Department of Fish and Game, Natural Diversity Data Base. 28 p. [23402] 11. Call, Mayo W. 1979. Habitat requirements and management recommendations for sage grouse. Denver, CO: U.S. Department of the Interior, Bureau of Land Management, Denver Service Center. 37 p. [591] 12. Call, Mayo W.; Maser, Chris. 1985. Wildlife habitats in managed rangelands--the Great Basin of southeastern Oregon: sage grouse. Gen. Tech. Rep. PNW-187. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 30 p. [592] 13. Dalke, Paul D.; Pyrah, Duane B.; Stanton, Don C.; [and others]. 1963. Ecology, productivity, and management of sage grouse in Idaho. Journal of Wildlife Management. 27(4): 810-841. [5975] 14. Dunkle, Sidney W. 1977. Swainson's hawks on the Laramie Plains, Wyoming. Auk. 94: 65-71. [22654] 15. Edminster, Frank C. 1947. The ruffed grouse: Its life story, ecology and management. New York: The MacMillan Company. 385 p. [25978] 16. Eng, Robert L.; Schladweiler, P. 1972. Sage grouse winter movements and habitat use in central Montana. Journal of Wildlife Management. 36: 141-146. [7529] 17. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 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. Gates, Robert J.; Eng, Robert L. 1984. Sage grouse, pronghorn, and lagomorph use of a sagebrush-grassland burn site on the Idaho National Engineering Laboratory. In: Markham, O. Doyle, ed. Idaho National Engineering Laboratory radio ecology and ecology programs: 1983 progress reports. Idaho Falls, ID: U.S. Department of Energy, Radiological and Environmental Sciences Laboratory: 220-235. [1005] 20. Gill, R. Bruce. 1966. A literature review on the sage grouse. Special Report No. 6. Denver, CO: Colorado Department of Game, Fish, and Parks, Game Research Division, Cooperative Wildlife Research Unit. 38 p. [26474] 21. Gregg, Michael A.; Crawford, John A.; Drut, Martin S.; DeLong, Anita K. 1994. Vegetational cover and predation of sage grouse nests in Oregon. Journal of Wildlife Management. 58(1): 162-166. [25626] 22. Griner, Lynn A. 1939. A study of the sage grouse (Centrocerus urophasianus) with special reference to life history, habitat requirements, & numbers & distributi. Logan, UT: Utah State Agricultural College. 111 p. Thesis. [Microfiche]. [26034] 23. Hamerstrom, Frederick; Hamerstrom, Frances. 1961. Status and problems of North American grouse. Wilson Bulletin. 73(3): 284-294. [15807] 24. Hargis, Christina; McCarthy, Clinton. 1986. Vegetation changes following a prescribed burn on a Great Basin meadow. In: Transactions of the Western Section of the Wildlife Society. 22: 47-51. [15955] 25. Hulet, Brian V.; Flinders, Jerran T.; Green, Jeffrey S.; [and others]. 1986. Seasonal movements and habitat selection of sage grouse in southern Idaho. In: McArthur, E. Durant; Welch, Bruce L., compilers. Proceedings--symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9-13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 168-175. [1206] 26. Ihli, Mike; Sherbenou, Phil; Welch, C. W. 1973. Wintering sage grouse in the upper Big Lost River. Transactions, Idaho Academy of Sciences. ?: 73-80. [8091] 27. Johnsgard, Paul A. 1973. Grouse and quails of North America. Lincoln, NE: University of Nebraska Press. 553 p. [20323] 28. Johnsgard, Paul A. 1983. The grouse of the world. Lincoln, NE: University of Nebraska. 413 p. [18404] 29. Kindschy, Robert R. 1986. Rangeland vegetative succession--implications to wildlife. Rangelands. 8(4): 157-159. [22] 30. Klebenow, Donald A. 1969. Sage grouse nesting and brood habitat in Idaho. Journal of Wildlife Management. 33(3): 649-662. [27322] 31. Klebenow, Donald A. 1973. The habitat requirements of sage grouse and the role of fire in management. In: Proceedings, annual Tall Timbers fire ecology conference; 1972 June 8-9; Lubbock, TX. No. 12. Tallahassee, FL: Tall Timbers Research Station: 305-315. [1345] 32. Kuchler, A. W. 1964. United States [Potential natural vegetation of the conterminous United States]. Special Publication No. 36. New York: American Geographical Society. 1:3,168,000; colored. [3455] 33. Mangan, Larry; Autenrieth, R. 1985. Vegetation changes following 2,4-D application and fire in a mountain big sagebrush habitat type. In: Sanders, Ken; Durham, Jack, eds. Rangeland fire effects: a symposium: Proceedings of the symposium; 1984 November 27-29; Boise, ID. Boise, ID: U.S. Department of the Interior, Bureau of Land Management, Idaho State Office: 61-65. [1519] 34. Martin, Alexander C.; Zim, Herbert S.; Nelson, Arnold L. 1951. American wildlife and plants. New York: McGraw-Hill Book Company, Inc. 500 p. [4021] 35. Martin, Neil S. 1970. Sagebrush control related to habitat and sage grouse occurrence. Journal of Wildlife Management. 34(2): 313-320. [26121] 36. Martin, Robert C. 1990. 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