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: Arctostaphylos pungens | Pointleaf Manzanita
 

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: Arctostaphylos pungens | Pointleaf Manzanita
ABBREVIATION : ARCPUN SYNONYMS : NO-ENTRY SCS PLANT CODE : ARPU5 COMMON NAMES : pointleaf manzanita Mexican manzanita TAXONOMY : The currently accepted scientific name of pointleaf manzanita is Arctostaphylos pungens H.B.K. (Ericaceae) [13,19,25,32]. LIFE FORM : Shrub FEDERAL LEGAL STATUS : NO-ENTRY OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : H. Harris, October 1988 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Harris, Holly T. 1988. Arctostaphylos pungens. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Arctostaphylos pungens | Pointleaf Manzanita
GENERAL DISTRIBUTION : Pointleaf manzanita is distributed from California, Nevada, and Utah to western Texas. Its range extends south into Mexico to the states of Chihuahua, Coahiula, Veracruz, and Oaxaca [12,19,25,32]. ECOSYSTEMS : FRES21 Ponderosa pine FRES28 Western hardwoods FRES34 Chaparral - mountain shrub STATES : AZ CA NV NM TX UT MEXICO ADMINISTRATIVE UNITS : CHIR CORO FOBO GRCA LAME PINN SAGU ZION BLM PHYSIOGRAPHIC REGIONS : 3 Southern Pacific Border 6 Upper Basin and Range 7 Lower Basin and Range 12 Colorado Plateau 13 Rocky Mountain Piedmont KUCHLER PLANT ASSOCIATIONS : K019 Arizona pine forest K030 California oakwoods K031 Oak - juniper woodlands K032 Transition between K031 and K037 K033 Chaparral K034 Montane chaparral K037 Mountain mahogany - oak scrub SAF COVER TYPES : 237 Interior ponderosa pine 241 Western live oak 247 Jeffrey pine 249 Canyon live oak SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Pointleaf manzanita is present in pine (Pinus spp.) forests and oak woodlands, but occurs most frequently in chaparral communities [22] Publications listing pointleaf manzanita as a dominant or codominant shrub layer species include: Classification of the forest vegetation on the National Forests of Arizona and New Mexico [1] Arizona chaparral: plant associations and ecology [3] Forest habitat types in the Apache, Gila, and part of the Cibola National Forests, Arizona and New Mexico [8] A habitat type classification system for ponderosa pine forests of northern Arizona [11] Forest and woodland habitat types (plant associations) of northern New Mexico and northern Arizona [17] The natural vegetation of Arizona [21]

VALUE AND USE

SPECIES: Arctostaphylos pungens | Pointleaf Manzanita
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Goats will graze pointleaf manzanita leaves, browse young twigs, and strip the bark for sap in the spring; new growth is occasionally used by deer [29]. Pase and Pond [23] report a 30 percent utilization rate of current year's growth on young pointleaf manzanita seedlings by cattle and deer on a 2-year-old burn site in Arizona. Pointleaf manzanita berries are found in the diets of skunks, coyotes, foxes, grouse, quail, bears, and deer [23,25,31,32]. Overall, the genus Arctostaphylos is considered low quality browse, and is indicative of range problems if heavily used [4]. PALATABILITY : Palatability of pointleaf manzanita is low for deer in all seasons and for all plant parts (leaves, twigs, fruit) [20]. Palatability for other animals has not been assessed. NUTRITIONAL VALUE : Food value of pointleaf manazanita has not been documented in the literature. COVER VALUE : Cover value of pointleaf manzanita has not been documented in the literature. VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : In Mexico, a jelly is made from unripe pointleaf manzanita fruits. The leaves and fruits are used as a remedy for stomach trouble, bronchitis, and venereal disease [4,14,29]. MANAGEMENT CONSIDERATIONS : Pointleaf manzanita may be used as an indicator of range condition; if heavily browsed, range problems are evident [4].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Arctostaphylos pungens | Pointleaf Manzanita
GENERAL BOTANICAL CHARACTERISTICS : Pointleaf manzanita is a short-lived, native evergreen shrub approximately of 5 to 7 feet (1.5 to 3 m) in height. Leaves are bright green, 1 inch long and 0.5 inch wide (3 x 1.5 cm); the bark is red-brown and smooth. Generally erect or ascending, the plant branches from the base to form thickets [5,12,13,32]. Decumbent branches often form roots, and may or may not break away from the mother plant [4,32]. Pointleaf manzanita does not form a basal burl [5,19]. The root system is shallow and fibrous; however, taproots are well-developed in sandy soil. While roots greater than 0.5 inch (1 cm) in diameter have been found in soil up to 20 inches (50 cm) deep, 65 percent of the root system exists in the top 8 inches (20 cm) of soil [16,31]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : In the absence of fire, pointleaf manzanita has grown to 20 feet in diameter at an estimated age of 50 years. Significant increases in size are the result of layering rather than sprouting. Lower branches lying on the ground take root and may break from the mother plant, resulting in a "fairyring" type of growth [22,24]. As the plant ages, it becomes unproductive; the central portion progressively dies while the periphery remains vigorous [22]. Seed germination occurs immediately after heat scarification by fire, allowing rapid revegetation in burned areas [3,4]. Pointleaf manzanita can by propagated by seeds sown in the fall in well-drained soil. Germination may be hastened by soaking seeds for 2 to 3 hours in sulfuric acid prior to planting. Germination averages 35 percent [32]. SITE CHARACTERISTICS : Pointleaf manzanita is found on dry, rocky slopes and mesas at elevations of 3,000 to 8,000 feet (900-2,400 m) throughout its range [12,13,19,32]. Upper limits of chaparral areas (7,000 ft) often border ponderosa pine associations, and pointleaf manzanita is commonly found in this transitional zone. Characteristically, chaparral is dry and warm; however, pointleaf manzanita may dominate relatively moist sites at higher elevations. Most precipitation in chaparral vegetational zones areas occurs as rain, with thunderstorms in summer and occasional snowfall at high elevations in winter; spring drought is common. Mean monthly precipitation varies from 0.39 inch (1 cm) in May to 3.7 inches (8 cm) in August and December. Temperatures vary from 41 degrees F (5 degrees C) in January to 77 degrees F (25 degrees C) in July. Soils in chaparral tend to be poorly developed, unstable, and coarse [22]. While chaparral occurs on a variety of parent rock material, pointleaf manzanita is known to grow on soils of granite and quartzite origins [3]. The ponderosa pine/pointleaf manzanita community type occurs on several different soil series and on gentle to steep slopes in northern Arizona [11]. Manzanitas (Arctostaphylos spp.) are characteristic in chihuahua pine/Arizona white oak (Pinus chihuahuana/Quercus arizonica) habitat types south of the Mogollon Rim in Arizona and New Mexico, where soils are lithic [6]. SUCCESSIONAL STATUS : Facultative Seral Species Pointleaf manzanita forms climax and seral chaparral communities in Arizona [3,22]. Seral communities may develop on ridges and steep slopes where higher temperatures and poor soils restrict pringle manzanita (A. pringlei) [22]. Hanks and others [11] described the ponderosa pine (Pinus ponderosa)/pointleaf manzanita community as late seral and/or a climax, but stated that successional status assessment of forest/chaparral types is difficult and arbitrary. Alexander and Ronco [1] list pointleaf manzanita as an indicator of climax pine (Pinus spp.) habitat types which burn frequently. On some sites, live oak (Quercus spp.) associations may replace pointleaf manzanita associations in the absence of fire [3,27]. Pointleaf manzanita seeds successfully germinate after fire, and plants live long enough to remain a component of communities throughout successional stages. SEASONAL DEVELOPMENT : Little is known about the phenology of pointleaf manzanita. Flowering generally occurs from January to March or April [4,19,25,32] with the fruit maturing from April to July [29,31,32].

FIRE ECOLOGY

SPECIES: Arctostaphylos pungens | Pointleaf Manzanita
FIRE ECOLOGY OR ADAPTATIONS : Unlike the many manzanita species, pointleaf manzanita does not sprout from the crown or roots following fire [3,4,22]. Pointleaf manzanita is an obligate seeder following fire, and prolific seed crops may be stored in the soil for decades [4,22]. Seeds readily germinate following heat scarification [3]. Pointleaf manzanita communities are characteristic of frequently burned areas with dry, coarse soils, and are typically found in the transition zone between chaparral and pine or oak woodlands [6,11]. Frequent fire prevents ponderosa pine/pointleaf manzanita communities from reaching climax in northern Arizona, and maintains them in a late seral stage [11]. POSTFIRE REGENERATION STRATEGY : Ground residual colonizer (on-site, initial community)

FIRE EFFECTS

SPECIES: Arctostaphylos pungens | Pointleaf Manzanita
IMMEDIATE FIRE EFFECT ON PLANT : Depending on fire severity, the mother plant is killed or greatly reduced by fire up to 6 years after burning [18,27]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Soil-stored seeds germinate following fire, resulting in numerous seedlings within 5 years [23]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Pointleaf manzanita depends on heat from fires for long-term survival as a species. In chaparral and dry pine forests, pointleaf manzanita has been susceptible to wildfire in the past; however, fire suppression in shrublands and forests in recent years has hindered its regenerative capabilities [22]. Areas dominated by non-sprouting chaparral species, including pointleaf manzanita, may develop a persistant cover of herbaceous species following fire [27].

REFERENCES

SPECIES: Arctostaphylos pungens | Pointleaf Manzanita
REFERENCES : 1. Alexander, Robert R.; Ronco, Frank, Jr. 1987. Classification of the forest vegetation on the National Forests of Arizona and New Mexico. Res. Note RM-469. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 10 p. [3515] 2. 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] 3. 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] 4. 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] 5. Correll, Donovan S.; Johnston, Marshall C. 1970. Manual of the vascular plants of Texas. Renner, TX: Texas Research Foundation. 1881 p. [4003] 6. DeVelice, Robert L.; Ludwig, John A. 1983. Forest habitat types south of the Mogollon Rim, Arizona and New Mexico. Final Report. Cooperative Agreement No. 28-K2-240 between U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station and New Mexico State University. Las Cruces, NM: New Mexico State University. 47 p. [780] 7. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 8. Fitzhugh, E. Lee; Moir, William H.; Ludwig, John A.; Ronco, Frank, Jr. 1987. Forest habitat types in the Apache, Gila, and part of the Cibola National Forests, Arizona and New Mexico. Gen. Tech. Rep. RM-145. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 116 p. [4206] 9. 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] 10. Hanes, Ted L. 1971. Succession after fire in the chaparral of southern California. Ecological Monographs. 41(1): 27-52. [11405] 11. Hanks, Jess P.; Fitzhugh, E. Lee; Hanks, Sharon R. 1983. A habitat type classification system for ponderosa pine forests of northern Arizona. Gen. Tech Rep. RM-97. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 22 p. [1072] 12. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of California. Berkeley, CA: University of California Press. 1400 p. [21992] 13. 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] 14. Krochmal, A.; Paur, S.; Duisberg, P. 1954. Useful native plants in the American Southwestern deserts. Economic Botany. 8: 3-20. [2766] 15. 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] 16. Kummerow, Jochen; Krause, David; Jow, William. 1977. Root systems of chaparral shrubs. Oecologia. 29: 163-177. [5352] 17. Larson, Milo; Moir, W. H. 1987. Forest and woodland habitat types (plant associations) of northern New Mexico and northern Arizona. 2d ed. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region. 90 p. [8947] 18. McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., eds. 1972. Wildland shrubs--their biology and utilization: An international symposium; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 494 p. [1612] 19. Munz, Philip A. 1974. A flora of southern California. Berkeley, CA: University of California Press. 1086 p. [4924] 20. Neff, Don J. 1974. Forage preferences of trained deer on the Beaver Creek watersheds. Special Report No. 4. Phoenix, AZ: Arizona Game and Fish Department. 61 p. [162] 21. Nichol, A. A. [revisions by Phillips, W. S.]. 1952. The natural vegetation of Arizona. Tech. Bull. 68 [revision]. Tucson, AZ: University of Arizona, Agricultural Experiment Station: 189-230. [3928] 22. 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] 23. 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] 24. 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] 25. 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] 26. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 27. Sampson, Arthur W. 1944. Plant succession on burned chaparral lands in northern California. Bull. 65. Berkeley, CA: University of California, College of Agriculture, Agricultural Experiment Station. 144 p. [2050] 28. 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] 29. Stubbendieck, J.; Hatch, Stephan L.; Hirsch, Kathie J. 1986. North American range plants. 3rd ed. Lincoln, NE: University of Nebraska Press. 465 p. [2270] 30. 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] 31. 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] 32. Vines, Robert A. 1960. Trees, shrubs, and woody vines of the Southwest. Austin, TX: University of Texas Press. 1104 p. [7707] 33. 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: Arctostaphylos pungens | Pointleaf Manzanita

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.