1Up Info - A Portal with a Difference

1Up Travel - A Travel Portal with a Difference.    
1Up Info
   

Earth & EnvironmentHistoryLiterature & ArtsHealth & MedicinePeoplePlacesPlants & Animals  • Philosophy & Religion  • Science & TechnologySocial Science & LawSports & Everyday Life Wildlife, Animals, & PlantsCountry Study Encyclopedia A -Z
North America Gazetteer


You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > Species: Prosopis pubescens | Screwbean Mesquite
 

Wildlife, Animals, and Plants

 


Wildlife, Animals, and Plants

 

Wildlife Species

  Amphibians

  Birds

  Mammals

  Reptiles

 

Kuchler

 

Plants

  Bryophyte

  Cactus

  Fern or Fern Ally

  Forb

  Graminoid

  Lichen

  Shrub

  Tree

  Vine


Introductory

SPECIES: Prosopis pubescens | Screwbean Mesquite
ABBREVIATION : PROPUB SYNONYMS : NO-ENTRY SCS PLANT CODE : PRPU COMMON NAMES : screwbean mesquite screwbean TAXONOMY : The currently accepted scientific name of screwbean mesquite is Prosopis pubescens Benth. [9,21,22,41]. LIFE FORM : Tree, Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Ronald Uchytil/June 1990 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Uchytil, Ronald J. 1990. Prosopis pubescens. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Prosopis pubescens | Screwbean Mesquite
GENERAL DISTRIBUTION : Screwbean mesquite is largely confined to valley bottomlands and its distribution often follows major water courses. In New Mexico and Texas, screwbean mesquite occurs along the Rio Grande from the Big Bend area northward to the town of Bernardo in central New Mexico [8,25]. Farther west it occurs in northern Baja California, throughout much of southeastern California, southern Nevada, eastern Arizona, and extreme southwestern Utah [25]. Its distribution is continuous along the Colorado River from about 50 miles (80 km) south of the Mexican-U.S. border northward to the Virgin River near Overton, Nevada [19,25]. Along the Virgin River, screwbean mesquite occurs northward to the Arizona-Utah border. Along the Gila River, screwbean mesquite has a continuous distribution eastward to midway between Florence and Kelvin, Arizona [19]. Along the Salt River, it occurs from the Salt River-Gila River confluence eastward to the Salt River Indian Reservation. A disjunct population occurs in the San Joaquin Valley of California. These plants became established between 1870 and 1890, probably from livestock-transported seed left along railways [20]. ECOSYSTEMS : FRES30 Desert shrub FRES33 Southwestern shrubsteppe FRES40 Desert grasslands STATES : AZ CA NV NM TX UT MEXICO ADMINISTRATIVE UNITS : BIBE DEVA GRCA GUMO JOTR LAME ORPI BLM PHYSIOGRAPHIC REGIONS : 7 Lower Basin and Range 13 Rocky Mountain Piedmont KUCHLER PLANT ASSOCIATIONS : K027 Mesquite bosque K041 Creosote bush K042 Creosote bush - bursage K043 Palo verde - cactus shrub K044 Creosote bush - tarbush K045 Ceniza shrub SAF COVER TYPES : 235 Cottonwood - willow 242 Mesquite SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : In general, screwbean mesquite only becomes a dominant or codominant in woodlands or scrublands along riparian zones. Associated trees and shrubs include saltcedar (Tamarix ramosissima), western honey mesquite (Prosopis glandulosa var. torreyana), velvet mesquite (P. velutina), seepwillow (Baccharis glutinosa), arroweed (Tessaria sericea), quailbush (Atriplex lentiformis), seepweed (Suaeda torreyana), skunkbrush sumac (Rhus trilobata), and wolfberry (Lycium andersonii) [8,31]. Along the Rio Grande, saltgrass (Distichlis spicata) and alkali sacaton (Sporobolus airoides) are common understory grasses [8].

VALUE AND USE

SPECIES: Prosopis pubescens | Screwbean Mesquite
WOOD PRODUCTS VALUE : Screwbean mesquite is cut for firewood [38]. Mesquite wood is easily sawed and split, is dry and heavy, ignites readily, and produces intense heat [18]. Screwbean mesquite is used locally for fenceposts and tool handles [23]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : The sweet-tasting bean pods of screwbean mesquite are high in protein and sugars and are avidly eaten by most livestock [10]. The fruit crop annually provides an abundant and nutritious food source for numerous wild animals. In general, mesquite (Prosopis spp.) seeds and beans form an important part of the diet of mice, kangaroo rats, woodrats, chipmunks, ground squirrels, rabbits, skunks, quail, doves, ravens, the porcupine, racoon, coyote, collared peccary, white-tailed deer, mule deer, wild turkey, and mallard [7,16,17,37]. Small rodents such as woodrats, kangaroo rats, and pocket mice derive a large portion of their diet from mesquite seeds [17]. Screwbean mesquite seeds are regularly eaten by the roadrunner and numerous species of quail [37,38]. Screwbean mesquite browse does not appear to be a particularly important wildlife food. Locally, screwbean mesquite browse is important to mule deer in California [16]. Jackrabbits probably consume large quantities of the leaves and bark, as they do with other mesquites (Prosopis spp.) [40]. PALATABILITY : The sweet, nutrituous seed pods of screwbean mesquite are highly palatable to all classes of livestock and to numerous small and large wildlife species. For both livestock and wildlife, the palatability of the leaves and twigs appears to be relatively low to moderate. NUTRITIONAL VALUE : Mesquite pods are nutritious. The thick and spongy pericarp is high in sugars and the seeds contain large amounts of protein. Nutritional information concerning screwbean mesquite fruit and seed is presented below [3]: % water % protein % fiber % ash % sugar whole pod 5.9 11.0 17.0 3.8 25.0 seeds 7.4 26.0 ---- --- ---- COVER VALUE : Screwbean mesquite tends to form thickets, which presumably provide needed security cover for large wildlife species like desert mule deer. Riparian communities dominated by screwbean mesquite provide important habitat for numerous bird species during both summer and winter [30] and essential nesting cover for numerous bird species [2]. Screwbean mesquite dominated bosques also provide favorable habitat for numerous small mammals such as pocket mice, deer mice, kangaroo rats, and woodrats. Many rodents place their burrows under the protective cover of mesquite shrubs [29]. VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : Screwbean mesquite was an important food item of Southwestern Native Americans. The beans were ground into flour which was used to prepare cakes and breads [4,12]. Various refreshing drinks were made from the sweet pods. Screwbean mesquite also provided fuel, shelter, weapons, tools, dyes and paints, medicines, cosmetics, baskets, furniture, clothing, rope, glue, and many other every day items [4]. MANAGEMENT CONSIDERATIONS : NO-ENTRY

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Prosopis pubescens | Screwbean Mesquite
GENERAL BOTANICAL CHARACTERISTICS : Screwbean mesquite is a deciduous, thorny shrub or small tree with slender branches. Plants range from 6.5 to 33 feet (2-10 m) tall. The trunk diameter on larger trees often reaches about 8 to 12 inches (20-30 cm) [28,38]. The smooth, thick, gray to reddish brown bark separates in long strips [28]. Single or paired, sharp, straight, white thorns occur at the base of the leaf stalks and are about 0.33 to 0.5 inch (8-12 mm) long [38]. The alternate, bipinnately compound leaves are 1.5 to 3 inches (3.8-7.6 cm) long and contain five to eight pairs of leaflets which are 0.25 to 0.38 inch (6-10 mm) long and 0.13 inch (3mm) wide [28]. The yellow flowers occur in 2-inch-long (5 cm) cylindrical spikes [32]. The fruit is a yellow to brown, 1- to 2-inch-long (2.5-5 cm) pod, which is tightly coiled into a springlike cylinder. Screwbean is easily distinguished from other common mesquites, such as velvet mesquite (P. velutina), honey mesquite (P. glandulosa var. glandulosa), and western honey mesquite (P. glandulosa var. torreyana), by its odd, screwlike pods and its considerably smaller leaves which have comparatively few, small leaflets [21]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Screwbean mesquite reproduces sexually by producing an abundance of seeds. Information regarding this species' vegetative regenerative capabilities is lacking. Other mesquites (Prosopis spp.) commonly sprout from buds located on an underground stem following injury to the aboveground portion of the plant [13,15]. Seed production: Mesquite flowers are pollinated by insects, predominately bees [35]. Screwbean mesquite's fruit production is probably rather consistent from year to year because plants are often found in riparian situations where they have access to subsurface water. Seed dispersal: Mesquite pods are dispersed primarily by domestic and wild animals. A large percentage of mesquite seeds pass through the digestive tracts of domestic animals intact and viable [13,15]. Many species of rodents collect and store mesquite beans in caches and uneaten seeds commonly. Mesquite pods may be carried downslope by running water [15]. Seed viability and germination: Mesquite seeds contain a bony, protective endocarp. Scarification of this hard seedcoat must occur before the seed can germinate. Scarification occurs naturally when seeds pass through the digestive system of animals. Seeds remaining in pods not consumed by animals remain dormant until the seedcoat is broken by weathering. Seeds remain dormant for long periods. Sixty percent viability was reported for 44-year-old velvet mesquite seeds taken from herbarium specimens [36]. Seedling establishment: Mesquite seeds must be covered with a small amount of soil or dung for seedlings to become established. Seeds that germinate on the soil surface usually die [15]. SITE CHARACTERISTICS : Screwbean mesquite is generally restricted to river bottoms, floodplains, washes, oases, and irrigation ditches where it tends to form thickets [20,21,33]. Shade tolerance: Screwbean mesquite apparently has moderate shade tolerance which allows plants to grow beneath cottonwoods (Populus spp.) [8]. Soils: Screwbean mesquite occurs on many soil textures, including gravels, sands, sandy-loams, and clays [8,37]. It often occurs on saline soils [23]. Elevation: Elevational ranges for the following Southwestern states are given below [23,32,41]: below 4,000 feet (1,219 m) in AZ below 2,500 feet (762 m) in CA from 2,400 to 5,450 feet (730-900 m) in UT SUCCESSIONAL STATUS : NO-ENTRY SEASONAL DEVELOPMENT : Screwbean mesquite flowers in the spring. The fruits mature between July and October and fall from the plant in autumn [10,37].

FIRE ECOLOGY

SPECIES: Prosopis pubescens | Screwbean Mesquite
FIRE ECOLOGY OR ADAPTATIONS : The underground regenerative structure of screwbean mesquite has not been described. Other mesquites of the American Southwest contain numerous dormant buds on an underground stem [13,15]. In general, these buds are sufficiently insulated to survive the heat of most fires. Riparian communities that have become dominated by saltcedar are highly flammable. One study of saltcedar stands along the lower Colorado River found that of 25 stands surveyed, 21 had burned within the past 15 years [42]. Although screwbean mesquite may survive these fires, it recovers slowly and is quickly overgrown by the saltcedar. With an increasing frequency of fire, screwbean mesquite will eventually be replaced [31,42]. POSTFIRE REGENERATION STRATEGY : NO-ENTRY

FIRE EFFECTS

SPECIES: Prosopis pubescens | Screwbean Mesquite
IMMEDIATE FIRE EFFECT ON PLANT : Most fires probably top-kill or kill screwbean mesquite. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Vogl and McHargue [39] report that plants not killed by fire resprout weakly. They further state that following a fire in a southern California oasis, a "dense stand" of screwbean mesquite and western honey mesquite was found under California palms (Washingtonia filifera) within 10 to 15 years. It is unclear whether these plants were established from seed or from individuals which survived the fire. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Prosopis pubescens | Screwbean Mesquite
REFERENCES : 1. Anderson, Bertin W.; Drake, Jeff; Ohmart, Robert D. 1977. Population fluctuations in nocturnal rodents in the lower Colorado River Valley. In: Johnson, R. Roy; Jones, Dale A., technical coordinators. Importance, preservation and management of riparian habitat: A symposium; 1977 July 9; Tucson, AZ. Gen. Tech. Rep. RM-43. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 183-193. Available from: NTIS, Springfield, VA 22151; PB-274 582. [5346] 2. Austin, George T. 1970. Breeding birds of desert riparian habitat in southern Nevada. Condor. 72: 431-436. [10874] 3. Becker, Robert. 1982. The nutritive value of Prosopis pods. In: Parker, Harry W., editor. Mesquite utilization 1982: Proceedings of the symposium; 1982 October 29-30; Lubbock, TX. Lubbock, TX: Texas Tech University, College of Agricultural Sciences: M-1-M-9. [5453] 4. Bell, Willis H.; Castetter, Edward F. 1937. Ethnobiological studies in the American Southwest: the utilization of mesquite and screwbean by the aborigines in the American Southwest. Biological Series 5(2). Albuquerque, NM: University of New Mexico. 55 p. [10033] 5. Benson, Lyman. 1941. The mesquites and screw-beans of the United States. American Journal of Botany. 28: 748-754. [5016] 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. Bogusch, E. R. 1950. A bibliography on mesquite. Texas Journal of Science. 4: 528-538. [5166] 8. Campbell, C. J.; Dick-Peddie, W. A. 1964. Comparison of phreatophyte communities on the Rio Grande in New Mexico. Ecology. 45(3): 492-502. [7003] 9. 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] 10. Dayton, William A. 1931. Important western browse plants. Misc. Publ. 101. Washington, DC: U.S. Department of Agriculture. 214 p. [768] 11. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 12. Felger, R. S. 1977. Mesquite in Indian cultures of southwestern North America. In: Simpson, B. B., ed. Mesquite: Its biology in two desert ecosystems. US/IBP Synthesis 4. Stroudsburg, PA: Dowden, Hutchinson & Ross, Inc: 150-176. [5195] 13. Fisher, C. E.; Meadors, C. H.; Behrens, R.; [and others]. 1959. Control of mesquite on grazing lands. Bull. 935. College Station, TX: Texas Agricultural Experiment Station. 24 p. In cooperation with: U.S. Department of Agriculture. [10078] 14. 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] 15. Glendening, George E.; Paulsen, Harold A., Jr. 1955. Reproduction and establishment of velvet mesquite as related to invasion of semidesert grasslands. Tech. Bull. 1127. Washington, DC: U.S. Department of Agriculture, Forest Service. 50 p. [3930] 16. Graham, Edward H. 1941. Legumes for erosion control and wildlife. Misc. Publ. 412. Washington, DC: U.S. Department of Agriculture. 153 p. [10234] 17. Gullion, Gordon W. 1964. Wildlife uses of Nevada plants. Contributions toward a flora of Nevada No. 49. Beltsville, MD: U. S. Department of Agriculture, Agricultural Research Service, National Arboretum Crops Research Division. 170 p. [6729] 18. Haller, John M. 1980. The indomitable mesquite. American Forests. 86(8): 20-23, 50-51. [5488] 19. 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] 20. Holland, Dan C. 1987. Prosopis (Mimosaceae) in the San Joaquin Valley, California: vanishing relict of recent invader?. Madrono. 34(4): 324-333. [3860] 21. Isely, D. 1973. Prosopis. New York Botanical Garden. 25(1): 116-122. [9891] 22. 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] 23. 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] 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. 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] 26. 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] 27. 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] 28. MacMahon, James A. 1988. Warm deserts. In: Barbour, Michael G.; Billings, William Dwight, eds. North American terrestrial vegetation. Cambridge; New York: Cambridge University Press: 231-264. [19547] 29. Mares, M. A.; Enders, F. A.; Kingsolver, J. M.; [and others]. 1977. Prosopis as a niche component. In: Simpson, B. B., ed. Mesquite: Its biology in two desert ecosystems. US/IBP Synthesis 4. Stroudsburg, PA: Dowden, Hutchinson & Ross, Inc: 123-149. [5194] 30. Meents, Julie K.; Anderson, Bertin W.; Ohmart, Robert D. 1984. Sensitivity of riparian birds to habitat loss. In: Warner, Richard E.; Hendrix, Kathleen M., eds. California riparian systems: Ecology, conservation, and productive management: Proceedings of a conference; 1981 September 17-19; Davis, CA. Berkeley, CA: University of California Press: 619-625. [5864] 31. Minckley, W. L.; Brown, David E. 1982. Wetlands. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 223-287. [8898] 32. Munz, Philip A. 1974. A flora of southern California. Berkeley, CA: University of California Press. 1086 p. [4924] 33. Parker, Kenneth W.; Martin, S. Clark. 1952. The mesquite problem on southern Arizona ranges. Circular No. 908. Washington, DC: U.S. Department of Agriculture. 70 p. [3350] 34. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 35. Simpson, B. B.; Neff, J. L.; Moldenke, A. R. 1977. Reproductive systems of Larrea. In: Mabry, T. J.; Hunziker, J. H.; DiFeo, D. R., Jr., eds. Creosote bush: Biology and chemistry of Larrea in New World deserts. U.S./IBP Synthesis Series 6. Stroudsburg, PA: Dowden, Hutchinson & Ross, Inc: 92-114. [7167] 36. Tschirley, Fred H.; Martin, S. Clark. 1960. Germination and longevity of velvet mesquite seed in the soil. Journal of Range Management. 13: 94-97. [9892] 37. 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] 38. Vines, Robert A. 1960. Trees, shrubs, and woody vines of the Southwest. Austin, TX: University of Texas Press. 1104 p. [7707] 39. Vogl, Richard J.; McHargue, Lawrence T. 1966. Vegetation of California fan palm oases on the San Andreas Fault. Ecology. 47(4): 532-540. [3044] 40. 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] 41. 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] 42. Anderson, Bertin W.; Higgins, Alton; Ohmart, Robert D. 1977. Avian use of saltcedar communities in the lower Colorado River Valley. In: Johnson, R. Roy; Jones, Dale A., technical coordinators. Importance, preservation and management of riparian habitat: A symposium; 1977 July 9; Tucson, AZ. Gen. Tech. Rep. RM-43. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 128-145. Available from NTIS, Springfield, VA 22151; PB-274 582. [5342] 43. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090] 44. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. [23104] 45. U.S. Department of the Interior, National Biological Survey. [n.d.]. NP Flora [Data base]. Davis, CA: U.S. Department of the Interior, National Biological Survey. [23119]

Index

Related categories for Species: Prosopis pubescens | Screwbean Mesquite

Send this page to a friend
Print this Page

Content on this web site is provided for informational purposes only. We accept no responsibility for any loss, injury or inconvenience sustained by any person resulting from information published on this site. We encourage you to verify any critical information with the relevant authorities.

Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

About Us | Contact Us | Terms of Use | Privacy | Links Directory
Link to 1Up Info | Add 1Up Info Search to your site

1Up Info All Rights reserved. Site best viewed in 800 x 600 resolution.