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: Mimosa biuncifera | Catclaw Mimosa
 

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: Mimosa biuncifera | Catclaw Mimosa
ABBREVIATION : MIMBIU SYNONYMS : Mimosa lindheimeri Mimosa prolifica Mimosopsis biuncifera SCS PLANT CODE : MIBI3 COMMON NAMES : catclaw mimosa catclaw wait-a-bit wait-a-minute wait-a-minute bush paired-thorn mimosa TAXONOMY : Catclaw mimosa is a legume a and member of the Mimosa Family, Mimosaceae. Its currently accepted scientific name is Mimosa biuncifera Benth. [2,21,23]. Catclaw mimosa exhibits a high degree of phenotypic variation and is often confused with, or mistaken for, other mimosas of the American Southwest. The taxonomy of catclaw mimosa and closely related species has been variously interpreted. The most recent taxonomic reevaluation has split catclaw mimosa into two species based on armature of the stem and pubescence of the corolla [2]. These two species and their synonyms are presented below [2]: Mimosa biuncifera Benth. = Mimosopsis biuncifera (Benth.) Britt. & Rose = Mimosa lindheimeri A. Gray = Mimosa biuncifera var. lindheimeri (A. Gray) B. L. Robinson = Mimosopsis lindheimeri (A. Gray) Britt. & Rose = Mimosa warnockii B. L. Turner. Mimosa texana (A. Gray) Small = Mimosa borealis var. texana A. Gray = Mimosa biuncifera var. lindheimeri sensu B. L. Turner, non (A. Gray) B. L. Robinson = Mimosopsis wherryana Britt. in Britt. & Rose = Mimosa wherryana (Britt.) Standl. = Mimosa lindheimeri var. pinnis 3-jugis A. Gray, Pl. Wright. LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Ronald Uchytil, November 1990 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Uchytil, Ronald J. 1990. Mimosa biuncifera. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Mimosa biuncifera | Catclaw Mimosa
GENERAL DISTRIBUTION : Catclaw mimosa occurs in central and southern Arizona, southern New Mexico, western and central Texas, and northern Mexico [18,39]. ECOSYSTEMS : FRES30 Desert shrub FRES32 Texas savanna FRES33 Southwestern shrubsteppe FRES34 Chaparral - mountain shrub FRES35 Pinyon - juniper FRES38 Plains grasslands STATES : AZ NM TX MEXICO ADMINISTRATIVE UNITS : AMIS BIBE CACA CHIR CORO FOBO GRCA GUMO LAMR MOCA SAGU BLM PHYSIOGRAPHIC REGIONS : 7 Lower Basin and Range 12 Colorado Plateau 13 Rocky Mountain Piedmont KUCHLER PLANT ASSOCIATIONS : K023 Juniper - pinyon woodland K031 Oak - juniper woodlands K032 Transition between K031 and K037 K043 Paloverde - cactus shrub K044 Creosotebush - tarbush K058 Grama - tobasa shrubsteppe K059 Trans-Pecos shrub savanna K085 Mesquite - buffalograss SAF COVER TYPES : 66 Ashe juniper - redberry (Pinchot) juniper 68 Mesquite 239 Pinyon - juniper 241 Western live oak SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Catclaw mimosa occurs in many vegetation types, generally as scattered plants intermixed with numerous other shrubs. It is occasionally the most abundant shrub. In low elevation desert grassland and shrub-steppe types, catclaw mimosa is often associated with other shrubby species, including mesquites (Prosopis spp.), redberry juniper, oneseed juniper (Juniperus monosperma), allthorn (Koeberlimia spinosa), catclaw acacia (Acacia greggii), larchleaf goldenweed (Haplopappus laricifolius), smooth sotol (Dasylirion leiophyllum), Wheeler sotol (D. wheeleri), lechuguilla (Agave lechuguilla), and goldeneye (Viguiera stenoloba) [11,25,36,37]. Catclaw mimosa is a common plant in the lower elevations of Arizona chaparral. Catclaw acacia and catclaw mimosa sometimes become abundant on drier, rockier, more open sites in Arizona chaparral [30]. Catclaw mimosa occurs as scattered individuals in oak, oak-pine, and evergreen woodlands with an overstory made up of one or more of the following trees: gray oak (Quercus grisea), Arizona white oak (Q. arizonica), Emory oak (Q. emoryi), Mohr's oak (Q. mohriana), Mexican pinyon (Pinus cembroides), pinyon pine (P. edulis), and alligator juniper (Juniperus deppeana) [12,17,29,40]. Associated shrubs in woodlands include fragrant sumac (Rhus aromatica), skunkbush sumac (R. trilobata), beargrass (Nolina microcarpa, N. erumperus), birchleaf mountain-mahogany (Cercocarpus betuloides), Wright silktassel (Garrya wrightii), yerba-de-pasmo (Baccharis pteronoides), and desert broom (Baccharis sarothroides) [12,29,40]. Published classification schemes listing catclaw mimosa as a indicator or dominant are listed below: Vegetation of the Organ Mountains, New Mexico [12] Woodland communities and soils of Fort Bayard, southwestern New Mexico [29]

VALUE AND USE

SPECIES: Mimosa biuncifera | Catclaw Mimosa
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Livestock seldom browse catclaw mimosa; however, it may be used lightly if other forage is scarce [20,39]. Livestock eat the pods [10]. Scaled and Gambel's quail eat the seeds [16]. It is of minor importance as a browse plant for deer and pronghorn [5,39]. PALATABILITY : Catclaw mimosa has dense prickles and a tangled growth form which may account for its relatively low palatability to livestock [10]. The pods are highly palatable to cattle, and the seeds are highly palatable to quail [10,16]. In western Texas, the palatability of catclaw mimosa has been rated good for pronghorn but poor for cattle and sheep [5]. NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : Catclaw mimosa has a tendency to form thickets, which presumably provide hiding and thermal cover for a variety of small wildlife species. Quail use such thickets [34]. VALUE FOR REHABILITATION OF DISTURBED SITES : Catclaw mimosa shows potential for erosion control. Plants have a tendency to form thickets which effectively bind soil [24,39]. OTHER USES AND VALUES : Catclaw mimosa flowers provide a good source of nectar for honey bees [39]. This plant has been studied as a source of biomass for the production of fuels and chemicals. In comparison with 100 other plant species examined, it yielded substantial amounts of oils, polyphenols, and hydrocarbons [8]. MANAGEMENT CONSIDERATIONS : Catclaw mimosa is moderately resistant to phenoxy herbicides [19].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Mimosa biuncifera | Catclaw Mimosa
GENERAL BOTANICAL CHARACTERISTICS : Catclaw mimosa is a relatively short, straggling, thicket-forming, deciduous shrub. It is usually not more than 3 feet (0.9 m) tall but occasionally grows up to about 8 feet (2.4 m) [6,24]. The pubescent, slender, straight to zig-zagging stems are armed with solitary or paired, stout, recurved spines [39]. The bipinnately compound leaves contain 3 to 9 pair of pinnae with 8 to 14 pairs of obtuse, linear to oblong, 0.04 to 0.17 inch (1.0-4.2 mm) long leaflets [39]. Numerous pale to whitish flowers occur in globose heads. The fruit is a curved or straight legume, 0.75 to 1.5 inch (1.9-3.8 cm) long, 0.13 to 0.17 inch (3.2-4.2 mm) wide, and is constricted between the seeds. RAUNKIAER LIFE FORM : Phanerophtye REGENERATION PROCESSES : Catclaw mimosa produces abundant seed. Seeds are encased within small, narrow pods that split open after ripening [34]. Primary dispersal agents have not been identified, but seed is probably dispersed by animals that eat the pods or seeds. Catclaw mimosa seeds exhibit high germination rates and germinate over a wide range of temperatures [22]. On the High Plains of west Texas, redberry juniper (Juniperus pinchottii) acts as a nurse plant for catclaw mimosa. The closed canopy and heavy mulch layer associated with redberry juniper apparently provides a favorable microenvironment for catclaw mimosa seedling establishment [28]. Catclaw mimosa sprouts from the root crown following damage to the aboveground portion of the plant, such as by fire or herbicides [19[. SITE CHARACTERISTICS : Catclaw mimosa occurs on gravelly flats, mesas, and rocky slopes in desert grass, desert shrub, interior chaparral, pinyon-juniper, open oak, and pine-oak communities [6,12,24,29,40]. Soils: In western Texas, catclaw mimosa often occupies soils derived from limestone or igneous rock [34]. Elevation: Elevational ranges are presented below [4,24,34]: from 2,000 to 5,000 feet (610-1,524 m) in w TX 3,000 to 6,000 feet (914-1,829 m) in AZ 4,300 to 5,600 feet (1,311-1,707 m) in the Rincon Mtns, se AZ SUCCESSIONAL STATUS : Catclaw mimosa is a common component of interior chaparral, a vegetation type considered to be a true climatic climax susceptible to large-scale burning [6]. This plant's sprouting ability allows it to become a part of the immediate postfire community. Individual plants may live to be very old, although the aboveground portion may date back only to the last fire [33]. Catclaw mimosa is considered an invader of desert and semiarid grasslands [20,34]. Fire suppression and livestock grazing are thought to be responsible for the spread of shrubs into what is considered to have been relatively shrub-free grasslands of the Southwest [41]. Although catclaw mimosa is fire tolerant and a high percentage of plants survive fire, a combination of frequent fires, droughts, competition, and browsing by rodents and lagomorphs may have suppressed plants in presettlement times [41]. Cattle reportedly "devour the pods" [10]. This undoubtedly has aided the spread of catclaw mimosa into grasslands because seeds are probably scarified as they pass through the digestive tract and are then deposited in nutrient-rich dung, which aids germination. SEASONAL DEVELOPMENT : The time of flowering for two Southwestern states is presented below: State Time of Flowering Authority AZ May - August [24] TX April - September [34]

FIRE ECOLOGY

SPECIES: Mimosa biuncifera | Catclaw Mimosa
FIRE ECOLOGY OR ADAPTATIONS : Catclaw mimosa is able to sprout from the root crown following top-kill by fire [6,20]. Hibbert and others [19] report that catclaw mimosa is fire tolerant and can rapidly recover by sprouting, even after repeated burns. Catclaw mimosa is common in Arizona chaparral. Severe wildfires are common in this vegetation type as a result of heavy fuel accumulation and scant early summer rainfall [31]. Fire frequencies are generally between 20 to 80 or 100 years, although some stands may experience longer fire-free intervals [6]. Most chaparral species are well adapted to fire and recover quickly. It takes at least 20 years before enough fuel accumulates to support a repeat fire, unless the area has been grass seeded [6]. POSTFIRE REGENERATION STRATEGY : Small shrub, adventitious-bud root crown

FIRE EFFECTS

SPECIES: Mimosa biuncifera | Catclaw Mimosa
IMMEDIATE FIRE EFFECT ON PLANT : Fires generally top-kill catclaw mimosa. By itself, it provides little fuel because of its open growth form and because its small leaves contribute very little to ground fuels when they drop [25]. However, the fuel of surrounding plants is often enough to ignite catclaw mimosa and cause its stems to burn off [25]. Catclaw mimosa commonly occurs in Arizona chaparral where wildfires are often severe, defoliating all aboveground vegetation and leaving only charred stems and a layer of ash over mineral soil [31]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Following top-kill by fire, catclaw mimosa survives by producing numerous sprouts from the root crown [6,20]. Because plants usually survive fire, density is generally not affected by burning. Although catclaw mimosa was not abundant in a study in desert mountain shrub vegetation in the Guadalupe Mountains, sampling of several 3- to 7-year-old burns showed that its frequency was greater on burned than on unburned sites [1]. Rapid regrowth allows plants to fully recover preburn cover within about 5 years [25,32]. Regrowth of top-killed catclaw mimosa plants was observed following several lightning- and man-caused fires in and near Carlsbad Caverns National Park, New Mexico. Here, top-killed plants sprouted and grew 8 to 10 inches (20-25 cm) in one growing season [25]. Following prescribed spring burns in desert grasslands and oak woodlands in southeastern Arizona, sprouts of catclaw mimosa regained 58 to 67 percent of plant preburn heights within two growing seasons as summarized below [3]. Emory oak/Arizona white oak desert grassland woodland date sampled mean height of plants mean height of plants burned area control area burned area control area inches/cm inches/cm inches/cm inches/cm Aug 1983 (prefire) 21.8/55.4 17.8/45.4 25.2/63.9 18.7/47.4 Aug 1984 (3 months 8.9/22.6 17.5/44.7 4.9/12.5 11.5/29.2 postfire) Aug 1985 (15 months 14.6/37.0 16.4/41.7 14.6/37.0 15.8/40.1 postfire) DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Mimosa biuncifera | Catclaw Mimosa
REFERENCES : 1. Ahlstrand, Gary M. 1982. Response of Chihuahuan Desert mountain shrub vegetation to burning. Journal of Range Management. 35(1): 62-65. [296] 2. Barneby, Rupert C.; Isely, Duane. 1986. Reevaluation of Mimosa biumcifera and M. texana (Leguminosae: Mimosoideae). Brittonia. 38(2): 119-122. [12230] 3. Bock, Jane H.; Bock, Carl E. 1987. Fire effects following prescribed burning in two desert ecosystems. Final Report on Cooperative Agreement No. 28-03-278. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 20 p. [12321] 4. Bowers, Janice E.; McLaughlin, Steven P. 1987. Flora and vegetation of the Rincon Mountains, Pima County, Arizona. Desert Plants. 8(2): 50-94. [495] 5. 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] 6. 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] 7. 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] 8. Carr, Merle E.; Mason, Charles T., Jr.; Bagby, Marvin O. 1986. Renewable resources from Arizona trees and shrubs. Forest Ecology and Management. 16: 155-167. [3053] 9. Correll, Donovan S.; Johnston, Marshall C. 1970. Manual of the vascular plants of Texas. Renner, TX: Texas Research Foundation. 1881 p. [4003] 10. Dayton, William A. 1931. Important western browse plants. Misc. Publ. 101. Washington, DC: U.S. Department of Agriculture. 214 p. [768] 11. Dick-Peddie, William A.; Alberico, Michael S. 1977. Fire ecology study of the Chisos Mountains, Big Bend National Park, Texas: Phase I. CDRI Contribution No. 35. Alpine, TX: The Chihuahuan Desert Research Institute. 47 p. [5002] 12. Dick-Peddie, W. A.; Moir, W. H. 1970. Vegetation of the Organ Mountains, New Mexico. Science Series No. 4. Fort Collins, CO: Colorado State University, Range Science Department. 28 p. [6699] 13. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 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. Gehlbach, Frederick R. 1967. Vegetation of the Guadalupe Escarpment, New Mexico-Texas. Ecology. 48(3): 404-419. [5149] 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. 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] 18. 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] 19. 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] 20. Humphrey, Robert R. 1960. Arizona range grasses: Description--forage value--management. Tucson, AZ: University of Arizona, Agricultural Experiment Station. 104 p. [5004] 21. Isely, Duane. 1971. Legumes of the United States. IV. Mimosa. American Midland Naturalist. 85(2): 410-424. [12980] 22. Jordan, Gilbert L.; Haferkamp, Marshal R. 1989. Temperature responses and calculated heat units for germination of several range grasses and shrubs. Journal of Range Management. 42(1): 41-45. [6083] 23. 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] 24. 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] 25. Kittams, Walter H. 1973. Effect of fire on vegetation of the Chihuahuan Desert region. In: Proceedings, annual Tall Timbers fire ecology conference; 1972 June 8-9; Lubbock, Texas. No. 12. Tallahassee, FL: Tall Timbers Research Station: 427-444. [6271] 26. 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] 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. McPherson, Guy R.; Wright, Henry A.; Wester, David B. 1988. Patterns of shrub invasion in semiarid Texas grasslands. American Midland Naturalist. 120(2): 391-397. [7197] 29. Medina, Alvin L. 1987. Woodland communities and soils of Fort Bayard, southwestern New Mexico. Journal of the Arizona-Nevada Academy of Science. 21: 99-112. [3978] 30. Pase, Charles P.; Brown, David E. 1982. Interior chaparral. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 95-99. [1826] 31. 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] 32. Pase, Charles P.; Pond, Floyd W. 1964. Vegetation changes following the Mingus Mountain burn. Res. Note RM-18. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 8 p. [5700] 33. Pond, Floyd W. 1971. Chaparral: 47 years later. Res. Pap. RM-69. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 11 p. [1905] 34. 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] 35. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 36. Scifres, C. J. 1980. Mesquite - 68. In: Eyre, F. H., ed. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters: 71-72. [7089] 37. Brown, David E. 1982. Semidesert grassland. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 123-131. [3603] 38. 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] 39. Vines, Robert A. 1960. Trees, shrubs, and woody vines of the Southwest. Austin, TX: University of Texas Press. 1104 p. [7707] 40. Whittaker, R. H.; Niering, W. A. 1965. Vegetation of the Santa Catalina Mountains, Arizona: a gradient analysis of the south slope. Ecology. 46: 429-452. [9637] 41. Wright, Henry A.; Bailey, Arthur W. 1982. Fire ecology: United States and southern Canada. New York: John Wiley & Sons. 501 p. [2620] 42. 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] 43. 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: Mimosa biuncifera | Catclaw Mimosa

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.