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Introductory

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
ABBREVIATION : CERBET SYNONYMS : Cercocarpus montanus var. glaber (S. Wats.) F. L. Martin Cercocarpus montanus var. blancheae (Schneid.) F. L. Martin Cercocarpus montanus var. macrourus (Rydb.) F. L. Martin Cercocarpus betulaefolius Nutt. ex Hook. Cercocarpus parvifolius Nutt. SCS PLANT CODE : CEBE3 CEBEB CEBEM COMMON NAMES : birchleaf mountain-mahogany birchleaf cercocarpus western mountain-mahogany California mountain-mahogany TAXONOMY : Dispute over the taxonomic placement of Cercocarpus betuloides Nutt. has been considerable. Martin's [32] 1950 taxonomic revision of the genus Cercocarpus reduced C. betuloides to several varieties of C. montanus Raf. [see SYNONYMS above]. Some taxonomists have adopted Martin's revision [19,20,47], while others treat C. betuloides and C. montanus as distinct species [21,30,37]. In this report, C. betuloides is recognized as a distinct species, birchleaf mountain-mahogany, found in southern Oregon, California, and Arizona. Plants found in the Intermountain and Rocky Mountain regions are C. montanus, true mountain-mahogany. Munz [37] recognizes three varieties of birchleaf mountain-mahogany: var. betuloides var. blancheae (Schneid.) Little var. macrourus (Rydb.) Jeps. Plants on Santa Catalina Island off the coast of southern California were once considered a fourth variety, var. traskiae (Eastw.) Dunkle, but are now recognized as a distinct species: C. traskiae, Catalina mountain-mahogany [30,37]. LIFE FORM : Tree, Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Ronald Uchytil, November 1991 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Uchytil, Ronald J. 1991. Cercocarpus betuloides. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
GENERAL DISTRIBUTION : Birchleaf mountain-mahogany's range extends from southwestern Oregon south through California to Baja California, and east from southern California to the mountains of central Arizona [30]. In California, birchleaf mountain-mahogany is found primarily in the Coast Range, the western slope of the Sierra Nevada's, and in the mountains of southern California [5]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES28 Western hardwoods FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper STATES : AZ CA OR MEXICO ADMINISTRATIVE UNITS : CORO CHIS JOTR KICA PINN SAMO SEQU WACA WHIS BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains 3 Southern Pacific Border 4 Sierra Mountains 7 Lower Basin and Range KUCHLER PLANT ASSOCIATIONS : K009 Pine - cypress forest K010 Ponderosa shrub forest K023 Juniper - pinyon woodland K026 Oregon oakwoods K029 California mixed evergreen forest K030 California oakwoods K033 Chaparral K034 Montane chaparral K035 Coastal sagebrush K036 Mosaic of K030 and K035 SAF COVER TYPES : 233 Oregon white oak 238 Western juniper 239 Pinyon - juniper 240 Arizona cypress 245 Pacific ponderosa pine 247 Jeffrey pine 249 Canyon live oak 250 Blue oak - Digger pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Birchleaf mountain-mahogany is a primary component of many chaparral communities and is a dominant or codominant in localized areas. It is codominant with shrub live oak (Quercus turbinella) in Arizona chaparral. Other common associates in Arizona chaparral include desert ceanothus (Ceanothus greggii), Wright buckwheat (Rhamnus crocea), datil yucca (Yucca baccata), sugar sumac (Rhus ovata), hollyleaf buckthorn (Rhamnus crocea), broom snakewood (Gutierezia sarothrae), and Arizona oak (Quercus arizonica) [8]. In California chaparral, associates include eastwood manzanita (Arctostaphylos glandulosa), desert ceanothus, chaparral whitethorn (Ceanothus leucodermis), chamise (Adenostoma fasciculatum), scrub and live oaks (Quercus spp.), buckthorns (Rhamnus spp.), and sumacs (Rhus spp.) [5,17,35]. Published classifications listing birchleaf mountain-mahogany as a dominant in community types (cts) or plant associations (pas) are listed below: Area Classification Authority AZ chaparral pas Carmichael & others 1978 s CA: San Bernardino Mtns general veg. cts Minnich 1976

VALUE AND USE

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Birchleaf mountain-mahogany is a valuable browse for ungulates. In California, it is listed as one of primary browse species of deer in the north and south Coast Ranges, along the west slope of the Sierra Nevada, and in the southern mountain ranges [4]. Mule deer and white-tailed deer consumption of birchleaf mountain-mahogany is light to heavy in the late fall, winter, and spring [4,29,33]. PALATABILITY : In California, birchleaf mountain-mahogany's palatability is rated as good for cattle, good to excellent for sheep and goats, poor to good for horses, excellent for mule deer, and good for bighorn sheep [9,42]. NUTRITIONAL VALUE : Birchleaf mountain-mahogany is a nutritious ungulate browse. The protein content of leaves and twigs is somewhat higher than that of many associated browse species [41,42]. Seasonal variation in birchleaf mountain-mahogany twig and leaf chemical constituents has been reported [2,41,46]. COVER VALUE : Birchleaf mountain-mahogany presumably provides cover for a wide variety of animals, both in chaparral and forest communities. VALUE FOR REHABILITATION OF DISTURBED SITES : Birchleaf mountain-mahogany's ability to survive on harsh sites makes it a useful candidate for erosion control of arid mountain slopes [10]. Its use in rehabilitation projects, however, has been very limited due to problems with seedling establishment. Work with true mountain-mahogany suggests that plants can be established via fall planting [39]. Selective breeding within the Cercocarpus genus may provide crosses useful for rehabilitation work. Monsen and Davis [36] suggest that hybrids of true and birchleaf mountain-mahogany would retain the favorable adaptive traits of their parents, including nondormant seeds and an improved growth rate. OTHER USES AND VALUES : Native Americans used the strong wood of birchleaf mountain-mahogany to make fish spears, arrow shafts, and digging sticks. They used the inner bark for many medicinal purposes and to produce a purple dye [9]. MANAGEMENT CONSIDERATIONS : Biological control: Browsing by domestic goats can reduce brush growth. Studies in Arizona and California show that birchleaf mountain-mahogany is highly preferred by goats, and that managed herds can keep this plant closely browsed [16,27]. In Arizona, birchleaf mountain-mahogany height in browsed areas was 67 percent less than in unbrowsed areas [27]. Chemical control: Phenoxy herbicides have generally been ineffective in controlling sprouting chaparral shrubs. Fenuron and picloram applied to the soil as pellets are more effective, killing 54 and 94 percent of birchleaf mountain-mahogany, respectively, 3 years after application [7].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
GENERAL BOTANICAL CHARACTERISTICS : Birchleaf mountain-mahogany is an erect, open shrub or small tree. Plants are typically 5 to 12 feet (1.5-3.6 m) tall but occasionally grow up to 20 feet (6 m) [42]. Birchleaf mountain-mahogany height varied as follows in different aged chaparral stands in southern California [17]: coastal chaparral desert chaparral (feet) (meters) (feet) (meters) Stand age 2-8 years 5.2 1.6 4.6 1.4 9-21 years 5.2 1.6 7.8 2.4 22-40 years 6.6 2.0 7.5 2.3 40+ years 7.2 2.2 9.1 2.7 Mature birchleaf mountain-mahogany plants typically have considerable amounts of dead branches [14]. Simple, alternate, wedge-shaped leaves, up to 1 inch (2.5 cm) long, are borne on spurlike branchlets [37]. Bark is smooth and gray. The fruit is a soft, hairy, tubular achene with a 2- to 3-inch-long (5-7.5 cm) feathery style at the tip [10]. RAUNKIAER LIFE FORM : Microphanerophyte Nanophanerophyte REGENERATION PROCESSES : Birchleaf mountain-mahogany begins producing seed at about 10 years of age. Seed crops vary from very light to very heavy [3]. The seeds are not dormant and germinate readily without pretreatments. The fruit and awned-seeds are dispersed widely by wind, and occasionally by animals [10]. Seedling establishment is infrequent and is probably substantial only in years of high precipitation. Birchleaf mountain-mahogany sprouts vigorously from the root crown after top-killing disturbances [3]. SITE CHARACTERISTICS : Birchleaf mountain-mahogany occupies dry foothills and lower mountain slopes and ridges [9,21,42]. It is most abundant in chaparral vegetation types but is also common at its upper elevational limits in the understory of pinyon-juniper (Pinus edulis, P. monophylla-Juniperus spp.), oak (Quercus wislizeni, Q. chrysolepis), and pine (Pinus ponderosa, P. sabiniana) woodlands [7,9,35]. In southern California, birchleaf mountain-mahogany occurs in both coastal (west of the mountain range crest) and desert chaparral stands (east of the crest) but generally makes up a greater percentage of the cover in desert chaparral. It is often associated with north-facing aspects. On coastal exposures it becomes more abundant with increasing elevation [17]. Elevational range is 3,000 to 6,500 feet (915-1,982 m) in Arizona, and 500 to 6,000 (152-1,829 m) in California [7,9]. SUCCESSIONAL STATUS : Birchleaf mountain-mahogany is a stable member of chaparral communities. The plant is a long-lived vigorous sprouter and neither a regime of frequent fires nor long fire-free periods will eliminate it. During long, fire-free intervals, birchleaf mountain-mahogany rejuvenates its canopy by resprouting, ensuring continuous recruitment of new stems from an established root crown [23]. Under a regime of frequent fires, postfire sprouting ensures little demographic change [18]. In Arizona, shrub live oak-birchleaf mountain-mahogany communities are considered climax types [8]. Burcham [6] reported that in certain situations in southern California, pinyon-juniper communities may be replaced by birchleaf mountain-mahogany and desert ceanothus following fire. SEASONAL DEVELOPMENT : Birchleaf mountain-mahogany has been variously described as evergreen, deciduous, and partly deciduous. In some areas it apparently loses 25 to 75 percent of its leaves each fall [3]. Flowering in California is from March to May [9], and in Arizona from March to July [21].

FIRE ECOLOGY

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
FIRE ECOLOGY OR ADAPTATIONS : Birchleaf mountain-mahogany sprouts from the root crown following top-kill by fire. Sprouting is usually the only method of postfire regeneration [24]. Seedling establishment occurs infrequently from seed blown onto the burn from off-site plants [18] or from on-site seeds that fall from the crown of lightly burned plants [4]. POSTFIRE REGENERATION STRATEGY : survivor species; on-site surviving root crown or caudex off-site colonizer; seed carried by wind; postfire years 1 and 2

FIRE EFFECTS

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
IMMEDIATE FIRE EFFECT ON PLANT : Plant: Most fires top-kill birchleaf mountain-mahogany. It is a common component of chaparral where severe wildfires often defoliate all aboveground vegetation and leave only charred stems and a layer of ash over mineral ash [15,48]. Birchleaf mountain-mahogany is a strong resprouter, and survival is usually high; however, 25 to 60 percent mortality has been observed following hot chaparral fires [26,44]. Seed: Birchleaf mountain-mahogany seeds are not heat-resistant and are easily destroyed by fire. Seeds on the ground are especially vulnerable to heat damage; seeds in the crown of lightly damaged plants may occasionally survive [4]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Birchleaf mountain-mahogany sprouts vigorously following fire, and recovery is relatively rapid. Sprouting is independent of the growing season and can begin as soon as 10 days after burning [34]. Sixty-four percent of preburn plants had sprouted within 4.5 months of an intense summer chaparral fire in southern California [38]. Sprouts grow rapidly. After one growing season, fire-borne sprouts in southern California were taller than those of associated shrubs, averaging between 12 and 27 inches (31-69 cm) tall [25]. Six to eight years after fire, birchleaf mountain-mahogany sprouts are often 5 or 6 feet (1.5-1.8 m) tall [11,17]. Sprouts have produced seed as early as 5 years after fire [3]. Small numbers of seedlings have been observed on some burns [17,25]. Mortality of postfire seedlings may be high. Sweeny [43] observed that about 75 percent of first year birchleaf mountain-mahogany seedlings were dead 4 years after fire. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Percentage of dead arial fuels is higher for birchleaf mountain-mahogany than for associates such as chamise, manzanitas, and scrub oak (Quercus dumosa). Nearly all of these dead fuels are consumed during fire. Birchleaf mountain-mahogany, however, contains less volatile fats, oils, and terpines than do many of its associates, and is therefore much less flammable [15]. During prescribed fires in southern California, chamise and manzanitas burned intensely, with 75 to 85 percent of live fuels consumed, while only 45 percent of birchleaf mountain-mahogany live fuels were consumed [14]. Birchleaf mountain-mahogany sprouts of fire origin are highly palatable to deer and livestock. Although birchleaf mountain-mahogany is generally resistant to browsing, excessive browsing can kill new sprouts [3,42].

REFERENCES

SPECIES: Cercocarpus betuloides | Birchleaf Mountain-Mahogany
REFERENCES : 1. 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] 2. Bissell, Harold D.; Strong, Helen. 1955. The crude protein variations in the browse diet of California deer. California Fish and Game. 41(2): 145-155. [10524] 3. Biswell, H. H.; Gilman, J. H. 1961. Brush management in relation to fire and other environmental factors on the Tehama deer winter range. California Fish and Game. 47(4): 357-389. [6275] 4. Biswell, H. H.; Schultz, A. M.; Hedrick, D. W. 1953. A possible method of increasing western mountain mahogany on game ranges. California Fish and Game. 39(2): 187-189. [16033] 5. Bolsinger, Charles L. 1989. Shrubs of California's chaparral, timberland, and woodland: area, ownership, and stand characteristics. Res. Bull. PNW-RB-160. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Experiment Station. 50 p. [7426] 6. Burcham, L. T. 1974. Fire and chaparral before European settlement. In: Rosenthal, Murray, ed. Symposium on living with the chaparral: Proceedings; 1973 March 30-31; Riverside, CA. San Francisco, CA: The Sierra Club: 101-120. [4669] 7. Cable, Dwight R. 1975. Range management in the chaparral type and its ecological basis: the status of our knowledge. Res. Pap. RM-155. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 30 p. [579] 8. Carmichael, R. S.; Knipe, O. D.; Pase, C. P.; Brady, W. W. 1978. Arizona chaparral: plant associations and ecology. Res. Pap. RM-202. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 16 p. [3038] 9. 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] 10. Deitschman, Glenn H.; Jorgensen, Kent R.; Plummer, A. Perry. 1974. Cercocarpus H.B.K. cercocarpus (mountain-mahogany). 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: 309-312. [7583] 11. Everett, Percy C. 1957. A summary of the culture of California plants at the Rancho Santa Ana Botanic Garden 1927-1950. Claremont, CA: The Rancho Santa Ana Botanic Garden. 223 p. [7191] 12. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 13. 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] 14. Green, Lisle R. 1970. An expermintal prescribed burn to reduce fuel hazard in chaparral. Res. Note PSW-216. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station. 6 p. [16164] 15. Green, Lisle R. 1982. Prescribed burning in the California Mediterranean ecosystem. In: Conrad, C. Eugene; Oechel, Walter C., technical coordinators. Proceedings of the symposium on dynamics and management of Mediterranean-type ecosystems; 1981 June 22-26; San Diego, CA. Gen. Tech. Rep. PSW-58. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 464-471. [6052] 16. Green, Lisle R.; Newell, Leonard A. 1982. Using goats to control brush regrowth on fuelbreaks. Gen. Tech. Rep. PSW-59. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station. 13 p. [10681] 17. Hanes, Ted L. 1971. Succession after fire in the chaparral of southern California. Ecological Monographs. 41(1): 27-52. [11405] 18. Hanes, Ted L.; Jones, Harold W. 1967. Postfire chaparral succession in southern California. Ecology. 48(2): 259-264. [9824] 19. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168] 20. Kartesz, John T.; Kartesz, Rosemarie. 1980. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume II: The biota of North America. Chapel Hill, NC: The University of North Carolina Press; in confederation with Anne H. Lindsey and C. Richie Bell, North Carolina Botanical Garden. 500 p. [6954] 21. Kearney, Thomas H.; Peebles, Robert H.; Howell, John Thomas; McClintock, Elizabeth. 1960. Arizona flora. 2d ed. Berkeley, CA: University of California Press. 1085 p. [6563] 22. Keeley, Jon E. 1981. Reproductive cycles and fire regimes. In: Mooney, H. A.; Bonnicksen, T. M.; Christensen, N. L.; [and others], technical coordinators. Fire regimes and ecosystem properties: Proceedings of the conference; 1978 December 11-15; Honolulu, HI. Gen. Tech. Rep. WO-26. Washington, DC: U.S. Department of Agriculture, Forest Service: 231-277. [4395] 23. Keeley, Jon E. 1986. Resilience of Mediterranean shrub communities to fires. In: Dell, B.; Hopkins, A. J. N.; Lamont B. B., editors. Resilience in Mediterranean-type ecosystems. Dordrecht, the Netherlands: Dr. W. Junk Publishers: 95-112. [9826] 24. Keeley, Jon E. 1987. Role of fire in seed germination of woody taxa in California chaparral. Ecology. 68(2): 434-443. [5403] 25. Keeley, Jon E.; Keeley, Sterling C. 1981. Post-fire regeneration of southern California chaparral. American Journal of Botany. 68(4): 524-530. [4660] 26. Kinucan, Edith Seyfert. 1965. Deer utilization of postfire chaparral shrubs and fire history of the San Gabiel Mountians. Los Angeles, CA: California State College, Los Angeles. 61 p. Thesis. [11163] 27. Knipe, Oren D. 1983. Effects of Angora goat browsing on burned over Arizona chaparral. Rangelands. 5(6): 252-255. [1363] 28. 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] 29. Leach, Howard R.; Hiehle, Jack L. 1956. Food habits of the Tehama deer herd. California Fish and Game. 43: 161-178. [6874] 30. 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] 31. 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] 32. Martin, Floyd L. 1950. A revision of Cercocarpus. Brittonia. 7(2): 91-111. [12586] 33. McCulloch, Clay Y. 1973. Part I: Seasonal diets of mule and white-tailed deer. In: Deer nutrition in Arizona chaparral and desert habitats. Special Report No. 3. Phoenix, AZ: Arizona Game and Fish Department: 1-37. [9894] 34. Menke, John W.; Villasenor, Ricardo. 1977. The California Mediterranean ecosystem and its management. In: Mooney, Harold A.; Conrad, C. Eugene, technical coordinators. Proc. of the symp. on the 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: 257-270. [4847] 35. Minnich, Richard A. 1976. Vegetation of the San Bernardino Mountains. In: Latting, June, ed. Symposium proceedings: plant communities of southern California; 1974 May 4; Fullerton, CA. Special Publication No. 2. Berkeley, CA: California Native Plant Society: 99-124. [4232] 36. McKone, Mark J. 1985. Reproductive biology of several bromegrasses (Bromus): breeding system, pattern of fruit maturation, and seed set. American Journal of Botany. 72(9): 1334-1339. [1618] 37. Munz, Philip A. 1973. A California flora and supplement. Berkeley, CA: University of California Press. 1905 p. [6155] 38. Plumb, T. R. 1961. Sprouting of chaparral by December after a wildfire in July. Technical Paper 57. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station. 12 p. [9799] 39. Plummer, A. Perry; Christensen, Donald R.; Monsen, Stephen B. 1968. Restoring big-game range in Utah. Publ. No. 68-3. Ephraim, UT: Utah Division of Fish and Game. 183 p. [4554] 40. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 41. Reynolds, Hudson G. 1967. Chemical constituents and deer use of some crown sprouts in Arizona chaparral. Journal of Forestry. 65(12): 905-908. [12057] 42. Sampson, Arthur W.; Jespersen, Beryl S. 1963. California range brushlands and browse plants. Berkeley, CA: University of California, Division of Agricultural Sciences, California Agricultural Experiment Station, Extension Service. 162 p. [3240] 43. Sweeney, James R. 1956. Responses of vegetation to fire: A study of the herbaceous vegetation following chaparral fires. Berkeley, CA: University of California Press. 249 p. [3776] 44. Tratz, Wallace Michael. 1978. Postfire vegetational recovery, productivity, and herbivore utilization of a chaparral-desert ecotone. Los Angeles, CA: California State University. 133 p. Thesis. [5495] 45. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of scientific plant names. Vol. 1. List of plant names. SCS-TP-159. Washington, DC. 416 p. [11573] 46. Urness, Philip J. 1973. Part II: Chemical analyses and in vitro digestibility of seasonal deer forages. In: Deer nutrition in Arizona chaparral and desert habitats. Special Report 3. Phoenix, AZ: Arizona Game and Fish Department: 39-52. [93] 47. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. [2944] 48. Pase, Charles P.; Granfelt, Carl Eric, tech. coords. 1977. The use of fire on Arizona rangelands. Arizona Interagency Range Committee Publication No. 4. [Place of publication unknown]: [Arizona Interagency Range Committe]. 15 p. [1827]

Index

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