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Introductory

WILDLIFE SPECIES: Neotoma cinerea | Bushy-Tailed Woodrat
ABBREVIATION : NECI COMMON NAMES : bushy-tailed woodrat packrat woodrat TAXONOMY : The currently accepted scientific name for the bushy-tailed woodrat is Neotoma cinerea (Ord). It is a member of the family Cricetidae. The 13 recognized subspecies are listed below [15,37]. N. cinerea cinerea N. cinerea acraia (Elliot) N. cinerea alticola (Hooper) N. cinerea arizonae (Merriam) N. cinerea cinnamomea J. A. Allen N. cinerea drummondii (Richardson) N. cinerea fusca True N. cinerea lucida Goldman N. cinerea macrodon Kelson N. cinerea occidentalis Baird N. cinerea orolestes Merriam N. cinerea pulla Hooper N. cinerea rupicola J. A. Allen ORDER : Rodentia CLASS : Mammal FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Julie L. Tesky, November 1994 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Tesky, Julie L. 1994. Neotoma cinerea. In: Remainder of Citation

WILDLIFE DISTRIBUTION AND OCCURRENCE

WILDLIFE SPECIES: Neotoma cinerea | Bushy-Tailed Woodrat
GENERAL DISTRIBUTION : Bushy-tailed woodrats occur from the Yukon Territory and Northwest Territories south to Arizona and New Mexico and from California east to the Black Hills, South Dakota and the Badlands of the upper Missouri River drainage area of South Dakota and Nebraska [22]. The specific ranges of the subspecies are listed below [15]: N. c. drummondii - Occurs from the Yukon Territory and Northwest Territories south to eastern British Columbia and western Alberta. N. c. occidentalis - Occurs from the Yukon Territory to Washington, the Cascade Range of Oregon, and northern Idaho. N. c. cinerea - Occurs from southeastern British Columbia, southern Alberta, and southwestern Saskatchewan south to central Idaho, western Wyoming, Montana, and western North Dakota. N. c. alticola - Occurs in southern Washington, Oregon, southern Idaho, northeastern Caliifornia, and northern Nevada. N. c. rupicola - Occurs from southeastern Montana and North Dakota to western Nebraska and northeastern Colorado. N. c. cinnomomea - Occurs in southwestern Wyoming, northeastern Utah, and northwestern Colorado. N. c. fusca - Occurs in the Coast Ranges of Washington and Oregon. N. c. pulla - Occurs from southwestern Oregon to northern California. N. c. acraia - Occurs from east-central California to southeastern Idaho, Utah, and northern Arizona. N. c. lucida - Occurs in southeastern California and southwestern Nevada. N. c. orolestes - Occurs from southeastern Montana and southwestern South Dakota to northern New Mexico. N. c. arizonae - Occurs in Utah, Colorado, New Mexico, and Arizona. N. c. macrodon - Occurs in east-central Utah. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir-spruce FRES24 Hemlock-Sitka spruce FRES25 Larch FRES26 Lodgepole pine FRES27 Redwood FRES28 Western hardwoods FRES29 Sagebrush FRES34 Chaparral-mountain shrub FRES35 Pinyon-juniper FRES36 Mountain grasslands FRES44 Alpine STATES :
AZ CA CO ID MT NE NV NM OR SD
UT WA WY WY

AB BC NT SK YK
BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 3 Southern Pacific Border 4 Sierra Mountains 5 Columbia Plateau 6 Upper Basin and Range 7 Lower Basin and Range 8 Northern Rocky Mountains 9 Middle Rocky Mountains 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K001 Spruce - cedar - hemlock forest K002 Cedar - hemlock - Douglas-fir forest K003 Silver fir - Douglas-fir forest K004 Fir - hemlock forest K005 Mixed conifer forest K006 Redwood forest K007 Red fir forest K008 Lodgepole pine - subalpine forest K010 Ponderosa shrub forest K011 Western ponderosa forest K012 Douglas-fir forest K013 Cedar - hemlock - pine forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest K016 Eastern ponderosa forest K017 Black Hills pine forest K018 Pine - Douglas-fir forest K019 Arizona pine forest K020 Spruce - fir - Douglas-fir forest K021 Southwestern spruce - fir forest K022 Great Basin pine forest K023 Juniper - pinyon woodland K024 Juniper steppe woodland K025 Alder - ash forest K028 Mosaic of K002 and K026 K029 California mixed evergreen forest K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K050 Fescue - wheatgrass K051 Wheatgrass - bluegrass K052 Alpine meadows and barren K055 Sagebrush steppe K056 Wheatgrass - needlegrass shrubsteppe K063 Foothills prairie SAF COVER TYPES : 205 Mountain hemlock 206 Engelmann spruce - subalpine fir 207 Red fir 208 Whitebark pine 209 Bristlecone pine 210 Interior Douglas-fir 211 White fir 212 Western larch 213 Grand fir 215 Western white pine 216 Blue spruce 217 Aspen 218 Lodgepole pine 220 Rocky Mountain juniper 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 231 Port-Orford-cedar 232 Redwood 234 Douglas-fir - tanoak - Pacific madrone 237 Interior ponderosa pine 238 Western juniper 239 Pinyon - juniper 244 Pacific ponderosa pine - Douglas-fir 245 Pacific ponderosa pine 247 Jeffrey pine 248 Knobcone pine SRM (RANGELAND) COVER TYPES : NO-ENTRY PLANT COMMUNITIES : Bushy-tailed woodrats inhabit a wide variety of life zones from the arctic-alpine to the Sonoran Desert. They have definite habitat preferences in particular regions, but the species as a whole appears to have a wide ecological amplitiude. Bushy-tailed woodrats in Canada inhabit open forests of Douglas-fir (Pseudotsuga menziesii) and ponderosa pine (Pinus ponderosa) [1]. In the southern Oregon Coast Range, bushy-tailed woodrats are more common in mixed-conifer forests along streams than in Douglas-fir forests [3,4]. In this area, bushy-tailed woodrats prefer shrub through closed sapling-pole red alder (Alnus rubra) stands, shrub through old-growth mixed conifer forests, and closed sapling-pole through old-growth temperate, high temperate, and coniferous wetland forests [3]. In northern California, Tevis [34] found that bushy-tailed woodrats were rare in the mixed-conifer forests of the Douglas-fir zone, but inhabited redwood (Sequoia sempervirens) forests. In the Sierra Nevada, bushy-tailed woodrats are widespread in rocky habitat in upper elevation coniferous forests. Here, they prefer early successional stages of Jeffrey pine (Pinus jeffreyi), red fir (Abies magnifica), and lodgepole pine (Pinus contorta) [30]. In the White Mountains of California, bushy-tailed woodrats have a patchy distribution above timberline among plant communities that typically include sagebrush (Artemisia spp.), wax currant (Ribes cereum), and scattered grasses [14]. In south-central Idaho on the upper Snake River Plain, bushy-tailed woodrats occupy the northern cold desert shrub biome in which basin big sagebrush (Artemisia tridentata ssp. tridentata) covers more than 90 percent of the area. Major plant associates are bottlebrush squirreltail (Elymus elymoides), winterfat (Krascheninnikovia lanata), and needle-and-thread (Stipa comata) [21]. In the spruce-fir (Picea spp.-Abies spp.) zone of northern Utah, bushy-tailed woodrats were found in meadow and quaking aspen (Populus tremuloides) seral stages at a subalpine site, but were not found in the fir or spruce-fir communities [27]. In the Piceance Basin of Colorado, bushy-tailed woodrats occurred in a rolling uplands area of sagebrush communities, true pinyon-Utah juniper (Pinus edulis-Juniperus osteosperma) communities, mixed mountain shrub communities, and bottomland sagebrush communities [17]. REFERENCES : NO-ENTRY

BIOLOGICAL DATA AND HABITAT REQUIREMENTS

WILDLIFE SPECIES: Neotoma cinerea | Bushy-Tailed Woodrat
TIMING OF MAJOR LIFE HISTORY EVENTS : Breeding season - Bushy-tailed woodrats breed from January to August. In Canada, the peak of the breeding season is generally between March and June [1]. In a laboratory study, bushy-tailed woodrats bred from February to July [9]. Social organization - Bushy-tailed woodrats occur in small family groups, which are often widely separated [3]. Males keep harems of one to three females. The males are territorial and aggressively defend both dens and foraging areas [1]. Harems appearently begin to form in groups of immigrating subadults during the year before breeding. Young males leave home areas by 2.5 months, but females remain home to breed there the next year [9]. Gestation period and litter size - The gestation period is 27 to 32 days. Litter size averages 3.5 young, but may vary from one to six [1,8]. In the laboratory, females may have up to seven litters in 1 year, but under favorable conditions in the wild, two litters may be produced during the same year about 2 months apart. In the northern part of their range, probably only one litter is produced each year. Some females experience postpartum oestrus and breed within 24 to 48 hours after parturition, while others may not breed until after the first litter is weaned [1]. Maturation of young - Young venture out of the nest at 22 days of age and are weaned between 25 and 30 days [1,9]. Maturation time seems to vary from one area to another. In Colorado, Finley [11] considered bushy-tailed woodrats mature at 4 months of age. During a laboratory study, Escherish [9] found that bushy-tailed woodrats mature between 5 and 10 months of age, and stated that bushy-tailed woodrats generally can breed the spring or summer after birth. According to Banfield [1], bushy-tailed woodrats in Canada are capable of breeding at about 11 months old. Clark and Stromberg [6] found that bushy-tailed woodrats in Wyoming do not breed until they are 2 years old. In a laboratory study, Egoscue [8] found that females born in late spring or summer began breeding later the following year and had fewer litters their first breeding season than females born early in the year. Dispersal - Dispersal of young may occur shortly after weaning or over several years. Dispersal distances of 1.4 to 2 miles (2.2-3.2 km) have been recorded [3]. Since the distribution of family groups is patchy and the families are generally well separated, dispersal of young is an important component of metapopulation viability. The ability to recolonize vacated habitats is necessary. Habits - Bushy-tailed woodrats are primarily nocturnal and are most active during the half hour after sunset and at dawn, year-round [1,9,30]. Longevity - Bushy-tailed woodrats may live to be 3 to 4 years of age [22]. PREFERRED HABITAT : Bushy-tailed woodrats are found from sea level to mountaintops up to 14,110 feet (4,300 m) elevation. They are associated primarily with rocky environments in mountainous country, inhabiting cliffs, talus, caves, river canyons, rocky streamsides, and rock outcrops [1,3,22]. In southwestern Oregon, bushy-tailed woodrats generally occur in heavily forested areas among rocks overgrown with vegetation. Buildings, old logs, and log piles suffice where rocks are scarce. In the transition zone between the Douglas-fir-western hemlock (Tsuga heterophylla) forest and mixed conifer forest in southwestern Oregon, bushy-tailed woodrats persist without rock outcrops or talus. There, streamside forests provide the best environment followed by closed sapling-pole stands of mixed conifers and old growth [3]. Home range - Most bushy-tailed woodrats will forage up to 450 feet (137 m) from the den; this constitutes a 15-acre (6.1-ha) home range. In southwestern Oregon, Carey [3] recorded movements of up to 1,250 feet (381 m) within trapping grids that were only 1,300 feet [396 m] wide, which suggests a maximum home range of about 110 acres (44.5 ha). The average maximum distance moved per individual was 280 feet (85.3 m). The minimum habitat needed per family group has been estimated as 80 acres (32.4 ha) [3]. It is rare to find more than one family group on a talus slope covering 2 to 5 acres (0.8-2.0 ha). Banfield [1] reported an average population density of one bushy-tailed woodrat to 20 acres (8.1 ha) in Canada. Dispersal corridors - Persistence of a bushy-tailed woodrat population often depends on corridors that connect family groups. Steamside zones might play a key role in providing dispersal corridors. Heavily timbered streamsides are characterized by a diversity of plant species and vertical diversity of vegetation that includes forbs, shrubs, and deciduous trees. These provide food and, together with the noise of the stream, some protection from predation. Mixed-conifer old growth may also be used as a dispersal corridor [3]. COVER REQUIREMENTS : In most areas, adequate rock cover is the most important resource for the bushy-tailed woodrat, especially in areas that have cold weather and heavy snowfall. In areas of mild climate, hollow trees, tree cavities, and fallen trees provide adequate cover [9]. Shelters - Bushy-tailed woodrats often build shelters on or near the ground [1,3,9,11]. Shelters are commonly found in rock crevices or burrows under overhanging rocks. Shelters may also be built in hollow trees, hollow logs, log piles, and burrows under logs. In the Oregon Coast Range, bushy-tailed woodrats occasionally build arboreal shelters up to 50 feet (15 m) above ground that are loosely constructed of sticks [3]. Shelters consist of two parts: the den (external structure) and the nest (internal nest cup). Bushy-tailed woodrats usually build a bulky den of sticks, bones, foliage, debris, and human artifacts [1,3]. The den serves as a defensive maze to ensure time to escape from a predator, and also provides an eating platform and a food drying platform [1]. Within these dens bushy-tailed woodrats build small, open, cuplike nests [3]. FOOD HABITS : Bushy-tailed woodrats have a varied diet of woody plants, mushrooms, berries, seeds, and herbage [3,9,22]. In fall, cuttings are gathered and stored in crevices or dens for winter use [6,22]. In the Pacific Northwest, bushy-tailed woodrats eat the leaves and cambium of Douglas-fir, Sitka spruce (Picea sitchensis), and western hemlock, the leaves of western redcedar (Thuja plicata), and the green parts of Pacific bleeding heart (Dicentra formosa), red elderberry (Sambucus racemosa ssp. pubens), waterleaf (Hydrophyllum spp.), trailing blackberry (Rubus ursinus), Himalaya blackberry (R. discolor), and many other species [3]. In Canada, bushy-tailed woodrats show a preference for the leaves of quaking aspen, cherry (Prunus spp.), rose (Rosa spp.), snowberry (Symphoricarpos spp.), currants (Ribes spp.), elderberries (Sambucus spp.), and willows (Salix spp.). The twigs and needles of western white pine (Pinus monticola), Douglas-fir, Engelmann spruce (Picea engelmannii), subalpine fir (Abies lasiocarpa), and junipers (Juniperus spp.), and the seeds and/or fruits of Douglas-fir, anemones (Anemone spp.), fireweed (Epilobium angustifolium), gentians (Gentianella spp.), honeysuckle (Lonicera spp.), cinquefoils (Potentilla spp.), gooseberries (Ribes spp.), raspberries (Rubus spp.), and elderberries are also eaten [1]. In the pinyon-juniper ecosystem of the Piceance basin of Colorado, woody plants accounted for over 75 percent of the bushy-tailed woodrat's diet. Bitterbrush (Purshia spp.) was the predominant food item. Big sagebrush (Artemisia tridentata) seemed to be avoided. Forbs were eaten, but composed less than 15 percent of the diet [17]. PREDATORS : Bushy-tailed woodrats are prey for many predators including the spotted owl (Strix occidentalis), great horned owl (Bubo virginianus), boreal owl (Aegolius funereus), red-tailed hawk (Buteo jamaicensis), goshawk (Accipiter gentilis) and other hawks, rattlesnakes (Crotalus spp.), American marten (Martes americana), bobcat (Lynx rufus), weasels (Mustela spp.), spotted skunk (Spilogale putorius), striped skunk (Mephitis mephitis), wolverine (Gulo gulo), foxes (Vulpes spp. and Urocyon spp.), coyote (Canis latrans), and wolf (Canis lupus) [1,3,9,18,22]. Within spotted owl home ranges, especially near nest groves, the rate of predation on bushy-tailed woodrats may be very high, since bushy-tailed woodrats consistute a major portion of the spotted owl prey base [3]. MANAGEMENT CONSIDERATIONS : NO-ENTRY REFERENCES : NO-ENTRY

FIRE EFFECTS AND USE

WILDLIFE SPECIES: Neotoma cinerea | Bushy-Tailed Woodrat
DIRECT FIRE EFFECTS ON ANIMALS : Bushy-tailed woodrats can probably escape most fires by taking refuge in rocky habitats. A study in California showed that during a prescribed fire, woodrats (Neotoma spp.) evaded harm by escaping to rock outcrops [19]. Woodrats that do not escape to these refugia may be killed by fire [33]. Bushy-tailed woodrats residing in riparian areas are probably protected by their habitat, which tends to burn infrequently and in a patchy pattern. HABITAT RELATED FIRE EFFECTS : Specific information was not available regarding the effects of fire on bushy-tailed woodrat habitat. Fire regimes vary in the communities in which bushy-tailed woodrats occur. For example, the mean fire-free interval for Douglas-fir communities in southwestern Montana is about 40 to 45 years [35]. Western hemlock forests along the coast have a fire-free interval of about 750 years. Before the arrival of European settlers, redwood forests burned about every 200 to 500 years [36]. Bushy-tailed woodrats are found in early successional through climax stages of succession. Their presence depends more on cover and food availability than on seral stage. In the spruce-fir zone of northern Utah, for example, bushy-tailed woodrats were found in meadows and aspen stands. These communities are commonly the first successional stages after fire [27]. In the Sierra Nevada, bushy-tailed woodrats often inhabit early successional stages of Jeffrey pine and lodgepole pine, which are commonly created by fire [2,23]. Some berry-producing plants which provide food for bushy-tailed woodrats such as blackberries, raspberries, and gooseberries, often thrive after fire [32]. However, severe, stand-destroying fires that consume the organic layer can kill the roots of many berry-producing shrubs, reducing the potential for sprouting and delaying revegetation [26,31] Mature trees and old growth are also used by bushy-tailed woodrats. In some areas of southwestern Oregon, where rocky environments are not available, bushy-tailed woodrats may use fire-created cavities in trees as nest sites. Carey [3] found a bushy-tailed woodrat den in an old-growth tree having a fire-scar opening 3 feet (0.9 m) high and 2 feet (0.6 m) wide at the base. FIRE USE : NO-ENTRY REFERENCES : NO-ENTRY

REFERENCES

WILDLIFE SPECIES: Neotoma cinerea | Bushy-Tailed Woodrat
REFERENCES : 1. Banfield, A. W. F. 1974. The mammals of Canada. Toronto, ON: University of Toronto Press. 438 p. [21084] 2. Bock, Carl E.; Bock, Jane H. 1977. Patterns of post-fire succession on the Donner Ridge burn, Sierra Nevada. In: Mooney, Harold A.; Conrad, C. Eugene, technical coordinators. Proceedings of the symposium of environmental consequences of fire and fuel management in Mediterranean ecosystems; 1977 August 1-5; Palo Alto, CA. Gen. Tech. Rep. WO-3. Washington, DC: U.S. Department of Agriculture, Forest Service: 464-469. [4896] 3. Carey, Andrew B. 1991. The biology of aboreal rodents in Douglas-fir forests. Gen. Tech. Rep. PNW-276. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 46 p. [18163] 4. Carey, Andrew B.; Horton, Scott P.; Biswell, Brian L. 1992. Northern spotted owls: influence of prey base and landscape character. Ecological Monographs. 62(2): 223-250. [21290] 5. Center, G. Scott; Casler, Bruce R.; Carey, Andrew B. 1991. Woodrat abundance in forests of the southern Oregon Coast Range. In: Ruggiero, Leonard F.; Aubry, Keith B.; Carey, Andrew B.; Huff, Mark H, technical coordinators. Wildlife and vegetation of unmanaged Douglas-fir forests: Proceedings of a symposium; 1989 March 29-31; Portland, OR. Gen. Tech. Rep. PNW-GTR-285. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station: 528. [23857] 6. Clark, Tim W.; Stromberg, Mark R. 1987. Mammals of Wyoming. Lawrence, KS: University of Kansas, Museum of Natural History. 314 p. [23861] 7. Clary, Warren P.; Medin, Dean E. 1992. Vegetation, breeding bird, and small mammal biomass in two high-elevation sagebrush riparian habitats. 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: 100-110. [19103] 8. Egoscue, Harold J. 1962. The bushy-tailed wood rat: a laboratory colony. Journal of Mammalogy. 43(3): 328-337. [24335] 9. Escherich, P. C. 1981. Soicial biology of the bushy-tailed woodrat, Neotoma cinerea. Univeristy of California Publications in Zoology. 110: 1-132. [23864] 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. Finley, Robert B., Jr. 1958. The woodrats of Colorado: distribution and ecology. University of Kansas Publications: Museum of Natural History. 10: 213-552. [23865] 12. 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] 13. Gashwiler, Jay S. 1959. Small mammal study in west-central Oregon. Journal of Mammalogy. 40(1): 128-139. [14005] 14. Grayson, Donald K.; Livingston, Stephanie D. 1989. High-elevation records for Neotoma cinerea in the White Mountains, California. Great Basin Naturalist. 49(3): 392-395. [23860] 15. Hall, E. Raymond; Kelson, Keith R. 1959. The mammals of North America, Volume II. New York: The Ronald Press Company. 79 p. [21460] 16. Halvorson, Curtis H. 1981. Small mammal populations. In: Debyle, Norbert V., ed. Clearcutting and fire in the larch/Douglas-fir forests of western Montana--a multifaceted research summary. Gen. Tech. Rep. INT-99. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 41-46. [18631] 17. Haufler, Jonathan B.; Nagy, Julius G. 1984. Summer food habits of a small mammal community in the pinyon-juniper ecosystem. Great Basin Naturalist. 44(1): 145-150. [23856] 18. Hayward, Gregory D.; Hayward, Patricia H.; Garton, Edward O. 1993. Ecology of boreal owls in the northern Rocky Mountains, U.S.A. Wildlife Monographs No. 124. Bethesda, MD: The Wildlife Society. 59 p. [22718] 19. Howard, W. E.; Fenner, R. L.; Childs, H. E., Jr. 1959. Wildlife survival in brush burns. Journal of Range Management. 12: 230-234. [247] 20. Jameson, E. W., Jr.; Peeters, Hans J. 1988. California mammals. Berkeley, CA: University of California Press. 403 p. [23863] 21. Johnson, Mark K.; Hansen, Richard M. 1979. Foods of cottontails and woodrats in south-central Idaho. Journal of Mammalogy. 60(1): 213-215. [23859] 22. Jones, J. Knox, Jr.; Armstrong, David M.; Hoffman, Robert S.; Jones, Clyde. 1983. Mammals of the Northern Great Plains. Lincoln, NE: University of Nebraska Press. 375 p. [23862] 23. Kilgore, Bruce M. 1976. Fire management in the National Parks: an overview. Proceedings, Montana Tall Timbers fire ecology conference and Intermountain Fire Research Council fire & land management symposium; 1974 October 8-10; Missoula, MT. No. 14. Tallahassee, FL: Tall Timbers Research Station: 45-57. [19020] 24. 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] 25. Medin, Dean E.; Clary, Warren P. 1989. Small mammal populations in a grazed and ungrazed riparian habitat in Nevada. Res. Pap. INT-143. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 6 p. [10530] 26. Racine, Charles H.; Johnson, Lawrence A.; Viereck, Leslie A. 1987. Patterns of vegetation recovery after tundra fires in northwestern Alaska, U.S.A. Arctic and Alpine Research. 19(4): 461-469. [6114] 27. Schimpf, David J.; Henderson, Jan A.; MacMahon, James A. 1980. Some aspects of succession in the spruce-fir forest zone of northern Utah. Great Basin Naturalist. 40(1): 1-26. [16443] 28. Scotter, George W.; Simmons, Norman M. 1974. Range extensions for the bushy-tailed wood rat in the Northwest Territories. Canadian Field-Naturalist. 88: 489-490. [23858] 29. Van Gelden, Richard George. 1982. Mammals of the National Parks. Baltimore, MD: Johns Hopkins University Press. 310 p. [20893] 30. Verner, Jared; Boss, Allan S., tech. coords. 1980. California wildlife and their habitats: western Sierra Nevada. Gen. Tech. Rep. PSW-37. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station. 439 p. [10237] 31. Viereck, L. A. 1983. The effects of fire in black spruce ecosystems of Alaska and northern Canada. In: Wein, Ross W.; MacLean, David A., eds. The role of fire in northern circumpolar ecosystems. New York: John Wiley and Sons Ltd.: 201-220. [7078] 32. Wright, Henry A. 1974. Range burning. Journal of Range Management. 27(1): 5-11. [2613] 33. Wright, Henry A.; Bailey, Arthur W. 1982. Fire ecology: United States and southern Canada. New York: John Wiley & Sons. 501 p. [2620] 34. Tevis, Lloyd, Jr. 1956. Responses of small mammal populations to logging of Douglas-fir. Journal of Mammalogy. 37(3): 189-196. [16233] 35. Arno, Stephen F.; Gruell, George E. 1983. Fire history at the forest-grassland ecotone in southwestern Montana. Journal of Range Management. 36(3): 332-336. [342] 36. Agee, James K. 1993. Fire ecology of Pacific Northwest forests. Washington, DC: Island Press. 493 p. [22247] 37. Hall, E. Raymond. 1981. The mammals of North America. 2nd ed. Vol. 2. New York: John Wiley and Sons. 1271 p. [14765]

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