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Introductory

SPECIES: Acacia greggii | Catclaw Acacia
ABBREVIATION : ACAGRE SYNONYMS : Senegalia greggii SCS PLANT CODE : ACGR COMMON NAMES : catclaw acacia catclaw cat's claw acacia Gregg acacia Gregg catclaw devils-claw devils-claw acacia paradise flower long-flowered catclaw Texas mimosa una de gato (claw of cat) TAXONOMY : The currently accepted scientific name of catclaw acacia is Acacia greggii Gray [10,27,29,62]. Recognized varieties include: var. greggii - glabrous leaflets - Texas var. arizonica - pubescent leaflets - sw New Mexico to California Catclaw acacia hybridizes with guajillo (A. berlandieri) [34]. LIFE FORM : Tree, Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Ronald Uchytil/July 1990 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Uchytil, Ronald J. 1990. Acacia greggii. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Acacia greggii | Catclaw Acacia
GENERAL DISTRIBUTION : Catclaw acacia is common over much of the northern Chihuahuan, Sonoran, and southern Mojave deserts. It occurs in southern and western Texas, southern New Mexico, southern and central Arizona, southern Nevada, extreme southwestern Utah, southeastern California, and northern Mexico [33]. ECOSYSTEMS : FRES30 Desert shrub FRES31 Shinnery FRES32 Texas savanna FRES33 Southwestern shrubsteppe FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES38 Plains grasslands FRES40 Desert grasslands STATES : AZ CA NV NM TX UT MEXICO ADMINISTRATIVE UNITS : BIBE CACA CORO FOBO GRCA GUMO JOTR LAME MOCA ORPI SAGU BLM PHYSIOGRAPHIC REGIONS : 7 Lower Basin and Range 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains KUCHLER PLANT ASSOCIATIONS : K023 Juniper - pinyon woodland K027 Mesquite bosque K031 Oak - juniper woodlands K032 Transition between K031 and K037 K041 Creosote bush K042 Creosote bush - bursage K043 Paloverde - cactus shrub K044 Creosote bush - tarbush K045 Ceniza shrub K054 Grama - tobosa prairie K058 Grama - tobosa shrubsteppe K059 Trans-Pecos shrub savanna K060 Mesquite savanna K061 Mesquite - acacia savanna K062 Mesquite - live oak savanna K065 Grama - buffalograss K071 Shinnery K085 Mesquite - buffalograss K086 Juniper - oak savanna SAF COVER TYPES : 66 Ash juniper - redberry (Pinchot) juniper 67 Mohrs ("shin") oak 68 Mesquite 239 Pinyon - juniper 241 Western live oak 242 Mesquite SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Catclaw acacia is generally not a dominant plant but occurs as scattered individuals in many plant communities. It attains its highest densities in desert washes where it may codominate. Catclaw acacia has not been listed as a dominant plant or habitat type indicator in any published classifications.

VALUE AND USE

SPECIES: Acacia greggii | Catclaw Acacia
WOOD PRODUCTS VALUE : Catclaw acacia wood is very strong. It is used locally for small household items, saddle frames, and occasionally as firewood [30,60]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : Livestock: Catclaw acacia is a poor forage for livestock. It may be browsed in the early spring when twigs are green but is otherwise seldom eaten [24]. Wildlife browse: Catclaw acacia is a preferred mule deer forage [50,51]. Seasonal consumption of catclaw acacia by mule deer near Tuscon, Arizona has been reported as follows [51]: Spring = 17.9 percent of diet (leaves) Summer = 1.9 percent of diet (leaves and fruit) Autumn = 11.2 percent of diet (leaves) Winter = 3.9 percent of diet (leaves) White-tailed deer eat small amounts of catclaw acacia browse [1,37]. Jackrabbits and cottontails regularly eat the leaves, bark, and twigs [20,61]. White-throated woodrats eat the leaves [20]. Seed and fruit: Catclaw acacia seeds are important in the diet of numerous birds. When available, seeds may comprise 25 to 50 percent of the scaled quail's diet in southwestern Texas [36]. Gambel's quail and white-winged doves also eat large amounts of the seeds [20]. Seeds and pods are eaten by ground squirrels and woodrats [20,36]. Collared peccaries eat large amounts of the freshly ripened fruit [13]. In southern Arizona, catclaw acacia fruits made up 2 percent of the white-tailed deer's summer diet, and 14 percent of the mule deer's summer diet [37]. When the highly palatable velvet mesquite (Prosopis velutina) fruits are abundant, mule deer eat less catclaw acacia fruit [51]. Plants infested with mistletoe (Phoradendron californicum) often attract frugivorous birds because mistletoe produces a large fruit crop. A study in southern Nevada found that 67 percent of all catclaw acacia plants at the study area were infected with mistletoe [4]. PALATABILITY : The palatability of catclaw acacia browse for livestock is poor. The fruits are highly palatable to big game animals such as deer and peccaries. The palatability of catclaw acacia for livestock and wildlife species in Arizona and Texas is rated as follows [8,25,37,51]: AZ TX Cattle poor poor Sheep ---- poor Pronghorn ---- fair Mule deer (browse) good ---- (fruit) good ---- White-tailed deer (browse) fair ---- (fruit) fair ---- Small mammals fair ---- Upland game birds (fruit) good good NUTRITIONAL VALUE : Catclaw acacia browse is a moderately good source of protein for hooved browsers [26,31,37,48]. Fruits provide a good source of phosphorus during summer when other forages are deficient in this element [37]. Nutritional composition of leaves, flowers, and new growth of catclaw acacia plants from southern Arizona is presented below [31]: % dry matter % protein % lignin % ash % cellulose Jan-Feb 52.07 13.19 10.51 5.78 27.02 Mar-April 45.21 12.29 9.67 5.98 32.16 May-June 47.12 13.81 10.42 6.43 27.93 July-Aug 59.32 11.29 9.75 9.3 36.63 Sept-Oct 51.9 14.43 10.25 5.98 32.45 Nov-Dec 47.55 13.45 11.48 5.55 32.64 Nutritional information for catclaw acacia leaves and twigs from southwestern Texas plants is presented below [26]: % water % ash % cell wall % phos % protein % DOM leaves (4/13) 69 4 ---- .41 30 83 leaves (5/24) 61 4 25 .27 21 78 leaves&twigs (6/28) 50 5 36 .13 19 62 leaves (7/27) 48 5 33 .15 17 62 Nutritional composition of catclaw acacia seeds from southwestern Texas is presented below [16]: % crude protein % P % Ca % Mg % K % Na 20.7 .35 .50 .24 1.24 .02 COVER VALUE : Songbirds nest within the branches of catclaw acacia [2,11]. Catclaw acacia sometimes forms thickets which provide hiding places for numerous small- to medium-sized mammals [60]. Quail use the plants for roosts [58]. Plants provide shade for domestic and wild animals. VALUE FOR REHABILITATION OF DISTURBED SITES : Catclaw acacia has shown varying success when transplanted onto disturbed sites. Near Globe, Arizona, survival of 90-day-old nursery-grown seedlings transplanted onto asbestos mill waste tailings capped with 2 feet (0.6 m) of topsoil was 100 percent after 3 years [45]. Conversely, when catclaw acacia seedlings were transplanted onto either copper mine tailings or overburden near Tucson, Arizona, they sufferred 100 percent mortality within 2 years [43]. Commercial catclaw acacia seed is not available. In California, seed collected in the field exhibited good germination without any special treatment and germinated readily in fall or spring [15]. Seedlings should be grown in tall containers because they rapidly develop a deep root system. Nursery grown seedlings attained a height of 4 to 15 inches (10-38 cm) in 16 months [15]. Seed collection methods have been detailed [63]. OTHER USES AND VALUES : Catclaw acacia flowers provide an important source of nectar for honey bees [30]. This plant is used for low maintenance landscaping [52]. Native peoples ground the beans into a flour to make mush, breads, and cakes [60]. MANAGEMENT CONSIDERATIONS : Catclaw acacia is an invader of semidesert grasslands and has increased in density on grazing lands. It is considered a range pest because it reduces forage for livestock and makes moving and handling cattle more difficult. Numerous herbicides are used for brush control in the Southwest. In general, catclaw acacia is moderately resistant to phenoxy herbicides and refoliates or resprouts from the base [23]. In southwestern Texas, combinations of picloram and dicambia severely defoliated catclaw acacia plants, but most resprouted within 30 months [28]. Its susceptibility to numerous herbicides has been summarized [5]. Mechanical brush control measures have also been described [39,57].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Acacia greggii | Catclaw Acacia
GENERAL BOTANICAL CHARACTERISTICS : Catclaw acacia frequently occurs as a 3 to 10 foot (0.9-3 m) tall shrub but may develop into an upright tree 25 to 30 feet (7.6-9.1 m) tall [55]. It is often thicket forming and has numerous spreading, slender, thorny branches [60]. The brown, stout, "clawlike" thorns are about 0.25 inch (0.63 cm) long. The bark is gray to black and about 0.125 inch (0.32 cm) thick. Numerous creamy-yellow flowers occur in 1.25 to 2.5 inch (3.1-6.3 cm) long spikes. The stiff and papery, gray-brown, legume-type fruits are 2 to 5.5 inches (5-14 cm) long, 0.5 to 0.75 inch (1.2-1.9 cm) wide, curved or contorted, flattened and constricted between the seeds [10,55]. RAUNKIAER LIFE FORM : Undisturbed State: Phanerophyte (microphanerophyte) Burned or Clipped State: Hemicryptophyte REGENERATION PROCESSES : Catclaw acacia reproduces sexually by producing an abundance of seeds. Vegetative regeneration (sprouting) occurs following damage to the aboveground portion of the plant. Catclaw acacia flowers are pollinated by insects. In general, Acacias begin to produce seed between 2 and 4 years of age [63]. Several, nearly circular, 0.2 to 0.35 inch (5-9 mm) diameter, dark brown seeds are encased within a legume-type fruit [42,62]. Catclaw acacia seeds are principally dispersed by wild animals which eat them [44]. The seeds have a hard seed coat and can probably remain viable for several years [63]. Germination has been reported at 60 percent [60]. SITE CHARACTERISTICS : Catclaw acacia occurs primarily in semidesert grasslands, brushy rangelands, Arizona chaparral dominated by turbinella oak (Quercus turbinella), and desert shrub communities. In the Sonoran and Mojave Deserts, it is largely confined to runnels and washes [21,54]. Away from the washes catclaw acacia occurs as scattered individuals. When found on the slopes of a bajada, it is often restricted to the upper bajada where available moisture is more abundant compared to middle or lower bajada situations [7]. Catclaw acacia was found to have the highest water requirements of several desert shrubs tested [37]. This may partially explain why catclaw acacia, although living in arid regions, is often confined to dry washes or stream bottoms with relatively shallow water tables. In the Chihuahuan Desert, catclaw acacia is more common outside of desert washes. It is common in canyons, on mountain slopes, and in desert shrub communities [12,46]. Associated species: Along washes in the Sonoran and Mojave Deserts, associated shrubs include mesquites (Prosopis spp.), whitethorn acacia (Acacia constricta), blue paloverde (Cercidium floridum), ironwood (Olneya tesota), desert willow (Chilopsis linearis), and canyon ragweed (Franseria ambrosioides) [27,54]. In Texas, catclaw acacia often grows with honey mesquite (Prosopis glandulosa var. glandulosa) [27]. Elevation: Catclaw acacia is generally found at elevations between 1,000 and 5,000 feet (305-1,524 m) [60]. SUCCESSIONAL STATUS : Catclaw acacia is an invader of desert grasslands. Its density has increased over the past 100 years probably as a result of overgrazing and reduced fire frequencies [21]. In the Mojave Desert of southern California, catclaw acacia was found to be a long-lived shrub characteristic of mature, undisturbed desert shrub communities [59]. However, in low elevation desert shrub communities in the Sonoran Desert near Tucson, Arizona, it was found to be short-lived. No plants older than 50 years were found, and most lived for only 20 to 32 years [19]. In the Chihuahuan Desert, following the erosion of surface soils which overlie very weather-tolerant Tornilla Clay, catclaw acacia is a midseral species, eventually giving way to climax vegetation dominated by creosotebush (Larrea divaricata) and tarbush (Flourensia cernua) [41]. SEASONAL DEVELOPMENT : In general, catclaw acacia flowers in May or June, and pods mature between July and September [55].

FIRE ECOLOGY

SPECIES: Acacia greggii | Catclaw Acacia
FIRE ECOLOGY OR ADAPTATIONS : Catclaw acacia is able to sprout from the root crown following top-kill by fire [9]. Hibbert and others [23] report that catclaw acacia is fire-tolerant and can rapidly recover by sprouting even after repeated burns. POSTFIRE REGENERATION STRATEGY : survivor species; on-site surviving root crown or caudex

FIRE EFFECTS

SPECIES: Acacia greggii | Catclaw Acacia
IMMEDIATE FIRE EFFECT ON PLANT : Fires generally top-kill catclaw acacia. In southern California, a July wildfire in a chaparral-desert ecotone resulted in nearly all catclaw acacia plants being charred and defoliated, but less than 10 percent of the plants were killed [53]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Following top-kill by fire, catclaw acacia survives by producing numerous sprouts from the root crown [25,49,53]. Following a July fire in a chaparral-desert ecotone in southern California, more than 90 percent of catclaw acacia plants survived by sprouting [53]. Similarly, a high percentage of plants resprouted following a fire in south-central Arizona [49]. Plants started sprouting within 2 months after the California fire. Regrowth following this southern California wildfire is summarized below [53]: Average length of sprouts Average # Mesic canyon Xeric ridge sprouts/plant (inches) (cm) (inches) (cm) 2 months after fire (Sept) 30 1.7 4.3 --- --- 4 months after fire (Nov) 90 8.6 21.8 5.7 14.6 7 months after fire (Feb) 89 10.1 25.7 7.0 17.8 10 months after fire (June) 166 13.0 33.0 4.8 12.1 DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Acacia greggii | Catclaw Acacia
REFERENCES : 1. Anthony, Robert G.; Smith, Norman S. 1977. Ecological relationships between mule deer and white-tailed deer in southeastern Arizona. Ecological Monographs. 47: 255-277. [9890] 2. Austin, George T. 1970. Breeding birds of desert riparian habitat in southern Nevada. Condor. 72: 431-436. [10874] 3. 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] 4. Blake, John G. 1984. A seasonal analysis of bird communities in southern Nevada. Southwestern Naturalist. 29(4): 463-474. [5849] 5. Bovey, Rodney W. 1977. Response of selected woody plants in the United States to herbicides. Agric. Handb. 493. Washington, DC: U.S. Department of Agriculture, Agricultural Research Service. 101 p. [8899] 6. Bowers, Janice E.; McLaughlin, Steven P. 1987. Flora and vegetation of the Rincon Mountains, Pima County, Arizona. Desert Plants. 8(2): 50-94. [495] 7. Bowers, Michael A. 1988. Plant associations on a Sonoran Desert bajada: geographical correlates and evolutionary source pools. Vegetatio. 74: 107-112. [4408] 8. Buechner, Helmut K. 1950. Life history, ecology, and range use of the pronghorn antelope in Trans-Pecos Texas. American Midland Naturalist. 43(2): 257-354. [4084] 9. 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] 10. Barneby, Rupert C. 1989. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 3, Part B: Fabales. Bronx, NY: The New York Botanical Garden. 279 p. [18596] 11. Davis, C. A.; Sawyer, P. E.; Griffing, J. P.; Borden, B. D. 1974. Bird populations in a shrub-grassland area, southeastern New Mexico. Bulletin 619. Las Cruces, NM: New Mexico State University, Agricultural Experiment Station. 29 p. [4548] 12. Denyes, H. Arliss. 1956. Natural terrestrial communities of Brewster County, Texas, with special reference to the distribution of the mammals. American Midland Naturalist. 55(2): 289-320. [10862] 13. Eddy, Thomas A. 1961. Foods and feeding patterns of the collared peccary in southern Arizona. Journal of Wildlife Management. 25: 248-257. [9888] 14. England, A. Sidney; Foreman, Larry D.; Laudenslayer, William F., Jr. 1984. Composition and abundance of bird populations in riparian systems of the California deserts. In: Warner, Richard E.; Hendrix, Kathleen M., eds. California riparian systems: Ecology, conservation, and productive management. Berkeley, CA: University of California Press: 694-705. [5870] 15. 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] 16. Everitt, James H. 1986. Nutritive value of fruits or seeds of 14 shrub and herb species from south Texas. Southwestern Naturalist. 31(1): 101-137. [5273] 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. Goldberg, Deborah E.; Turner, Raymond M. 1986. Vegetation change and plant demography in permanent plots in the Sonoran Desert. Ecology. 67(3): 695-712. [4410] 20. Graham, Edward H. 1941. Legumes for erosion control and wildlife. Misc. Publ. 412. Washington, DC: U.S. Department of Agriculture. 153 p. [10234] 21. Hastings, James R.; Turner, Raymond M. 1965. The changing mile: An ecological study of vegetation change with time in the lower mile of an arid and semiarid region. Tuscon, AZ: University of Arizona Press. 317 p. [10533] 22. Hastings, James R.; Turner, Raymond M.; Warren, Douglas K. 1972. An atlas of some plant distributions in the Sonoran Desert. Technical Reports on the Meteorology and Climatology of Arid Regions No. 21. Tuscon, AZ: University of Arizona, Institute of Atmospheric Physics. 255 p. [10534] 23. Hibbert, Alden R.; Davis, Edwin A.; Scholl, David G. 1974. Chaparral conversion potential in Arizona: Part I: water yield response and effects on other resources. Res. Pap. RM-126. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 36 p. [1144] 24. Humphrey, R. R. 1950. Arizona range resources. II. Yavapai County. Bull. 229. Tucson, AZ: University of Arizona, Agricultural Experiment Station. 55 p. [5088] 25. Humphrey, Robert R. 1953. Forage production on Arizona ranges. III. Mohave County: A study in range condition. Bulletin 244. Tucson, AZ: University of Arizona, Agricultural Experiment Station. 79 p. [4440] 26. Huston, J. E.; Rector, B. S.; Merrill, L. B.; Engdahl, B. S. 1981. Nutritional value of range plants in the Edwards Plateau region of Texas. Report B-1375. College Station, TX: Texas A&M University System, Texas Agricultural Experiment Station. 16 p. [4565] 27. Isely, D. 1973. Acacia. Memoirs of the New York Botanical Garden. 25(1): 10-74. [12229] 28. Jacoby, P. W.; Meadors, C. H.; Foster, M. A.; Hartmann, F. S. 1982. Honey mesquite control and forage response in Crane County, Texas. Journal of Range Management. 35: 424-426. [5465] 29. 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] 30. 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] 31. Krausman, Paul R.; Ordway, Leonard L.; Whiting, Frank M.; Brown, William H. 1990. Nutritional compostition of desert mule deer forage in the Picacho Mountains, Arizona. Desert Plants. 10(1): 32-34. [7259] 32. 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] 33. Little, Elbert L., Jr. 1976. Atlas of United States trees. Volume 3. Minor western hardwoods. Misc. Publ. 1314. Washington, DC: U.S. Department of Agriculture, Forest Service. 13 p. 290 maps. [10430] 34. 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] 35. 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] 36. Martin, Alexander C.; Zim, Herbert S.; Nelson, Arnold L. 1951. American wildlife and plants. New York: McGraw-Hill Book Company, Inc. 500 p. [4021] 37. 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] 38. McGinnies, W. G.; Arnold, Joseph F. 1939. Relative water requirement of Arizona range plants. Technical Bulletin No. 80. Tucson, AZ: University of Arizona, Agricultural Experiment Station: 167-246. [4441] 39. Meadors, C. H.; Fisher, C. E.; Haas, R. H.; Hoffman, G. O. 1973. Combinations of methods and maintenance control of mesquite. In: Mesquite: Growth and development, management, economics, control, uses. Research Monograph 1. College Station, TX: Texas A&M University, The Texas Agricultural Experiment Station: 53-59. [4685] 40. Morton, Howard, L.; Metto, Paul; Ogden, Phil R. 1971. Catclaw control in southern Arizona. Proceedings of the Western Society of Weed Science. 24: 12-13. [12164] 41. Muller, Cornelius H. 1940. Plant succession in the Larrea-Flourensia climax. Ecology. 21: 206-212. [4244] 42. Munz, Philip A. 1974. A flora of southern California. Berkeley, CA: University of California Press. 1086 p. [4924] 43. Norem, M. A.; Day, A. D.; Ludeke, K. L. 1982. An evaluation of shrub and tree species used for revegetating copper mine wastes in the south-western United States. Journal of Arid Environments. 5: 99-304. [1776] 44. Pendleton, Rosemary L.; Pendleton, Burton K.; Harper, Kimball T. 1989. Breeding systems of woody plant species in Utah. In: Wallace, Arthur; McArthur, E. Durant; Haferkamp, Marshall R., compilers. Proceedings--symposium on shrub ecophysiology and biotechnology; 1987 June 30 - July 2; Logan, UT. Gen. Tech. Rep. INT-256. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 5-22. [5918] 45. Perry, Hazel M.; Aldon, Earl F.; Brock, John H. 1987. Reclamation of an asbestos mill waste site in the southwestern United States. Reclamation and Revegetation Research. 6: 187-196. [2918] 46. Powell, A. Michael. 1988. Trees & shrubs of Trans-Pecos Texas including Big Bend and Guadalupe Mountains National Parks. Big Bend National Park, TX: Big Bend Natural History Association. 536 p. [6130] 47. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 48. Rautenstrauch, Kurt R.; Krausman, Paul R.; Whiting, Frank M.; Brown, William H. 1988. Nutritional quality of desert mule deer forage in King Valley, Arizona. Desert Plants. 8(4): 172-174. [2768] 49. Rogers, Garry F.; Steele, Jeff. 1980. Sonoran Desert fire ecology. In: Stokes, Marvin A.; Dieterich, John H., technical coordinators. Proceedings of the fire history workshop; 1980 October 20-24; Tucson, AZ. Gen. Tech. Rep. RM-81. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 15-19. [16036] 50. Severson, Kieth E.; Medina, Alvin L. 1983. Deer and elk habitat management in the Southwest. Journal of Range Management Monograph No. 2. Denver: Society for Range Management. 64 p. [2110] 51. Short, Henry L. 1977. Food habits of mule deer in a semi-desert grass-shrub habitat. Journal of Range Management. 30: 206-209. [9895] 52. Thornburg, Ashley A. 1982. Plant materials for use on surface-mined lands. SCS-TP-157. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 88 p. [3769] 53. 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] 54. Turner, Raymond M.; Brown, David E. 1982. Sonoran desertscrub. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 181-221. [2375] 55. U.S. Department of Agriculture, Forest Service. 1937. Range plant handbook. Washington, DC. 532 p. [2387] 56. 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] 57. Vallentine, John F. 1961. Important Utah range grasses. Extension Circular 281. Logan, UT: Utah State University. 48 p. [2937] 58. Van Dersal, William R. 1938. Native woody plants of the United States, their erosion-control and wildlife values. Washington, DC: U.S. Department of Agriculture. 362 p. [4240] 59. Vasek, Frank C. 1979. Early successional stages in Mojave Desert scrub vegetation. Israel Journal of Botany. 28: 133-148. [4579] 60. Vines, Robert A. 1960. Trees, shrubs, and woody vines of the Southwest. Austin, TX: University of Texas Press. 1104 p. [7707] 61. Vorhies, Charles T.; Taylor, Walter P. 1933. The life histories and ecology of jack rabbits, Lepus alleni and Lepus californicus ssp., in relation to grazing in Arizona. Technical Bulletin No. 49. Tucson, AZ: University of Arizona, Agricultural Experiment Station. 117 p. [9933] 62. 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] 63. Whitesell, Craig D. 1974. Acacia Mill. acacia. 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: 184-186. [66]

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