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CEGL001270 Larrea tridentata - Flourensia cernua Shrubland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Creosotebush - American Tarwort Shrubland

Colloquial Name: No Data Available

Hierarchy Level:  Association

Type Concept: This established, but minor, plant association of White Sands Missile Range occurs within both the Jornada del Muerto and Tularosa basins and has been described on Fort Bliss Military Reservation. Stands are found on lower alluvial slopes and upper basin bottoms at elevations of 1070 to 1520 m (3500-5000 feet). Slopes are usually less than 1% and occasionally have scattered rock or gravel on the surface. Flourensia cernua occurs most often on heavy, fine soils, while Larrea tridentata is adapted to a wide range of soils. Stands are characterized by a shrub layer codominated by Larrea tridentata and Flourensia cernua. The shrubs are tall, evenly distributed and typically form a moderately open canopy. Scattered Gutierrezia sarothrae, Opuntia macrocentra, and Prosopis glandulosa are often present. The grass layer is poorly represented, but can include scattered clumps of Sporobolus airoides between shrub canopies, or Muhlenbergia porteri growing underneath them. The forb layer is scattered and Acourtia nana is most common. Increases in Flourensia cernua were difficult to distinguish from increases in Larrea tridentata, as Larrea tridentata establishment often followed or quickly replaced Flourensia cernua in particular areas. Because Larrea tridentata exploits deeper water sources than Flourensia cernua, it may not be as vulnerable to drought.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: No Data Available

Similar NVC Types: No Data Available
note: No Data Available

Physiognomy and Structure: No Data Available

Floristics: From Muldavin et al. (2000b): Stands are characterized by a shrub layer codominated by Larrea tridentata and Flourensia cernua. The shrubs are tall, evenly distributed and typically form a moderately open canopy. Scattered Gutierrezia sarothrae, Opuntia macrocentra, and Prosopis glandulosa are often present. The grass layer is poorly represented, but can include scattered clumps of Sporobolus airoides between shrub canopies, or Muhlenbergia porteri growing underneath them. The forb layer is scattered and Acourtia nana is most common.

Dynamics:  Buffington and Herbel (1965) found that increases in Flourensia cernua were difficult to distinguish from increases in Larrea tridentata, as Larrea tridentata establishment often followed or quickly replaced Flourensia cernua in particular areas. Because Larrea tridentata exploits deeper water sources than Flourensia cernua, it may not be as vulnerable to drought (Montana et al. 1995).

Environmental Description:  From Muldavin et al. (2000b): Stands are found on lower alluvial slopes and upper basin bottoms at elevations of 1070 to 1520 m (3500-5000 feet). Slopes are usually less than 1% and occasionally have scattered rock or gravel on the surface. Flourensia cernua occurs most often on heavy, fine soils, while Larrea tridentata is adapted to a wide range of soils (Buffington and Herbel 1965, Gehlbach 1967, Laurenroth et al. 1994b, Van Devender 1995).

Geographic Range: From Muldavin et al. (2000b): This established, but minor, plant association of White Sands Missile Range occurs within both the Jornada del Muerto and Tularosa basins and has been described on Fort Bliss Military Reservation (Wood et al. 1998).

Nations: MX,US

States/Provinces:  MXCHH, MXCOA, NM, TX




Confidence Level: Low - Poorly Documented

Confidence Level Comments: No Data Available

Grank: G5?

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: ? Larrea tridentata - Flourensia cernua / Erioneuron pulchellum (Dick-Peddie 1993)
= Larrea tridentata - Flourensia cernua / Sparse PA (Muldavin et al. 1998a)
= Larrea tridentata / Sparse Community Type, Flourensia cernua Phase (Muldavin et al. 1994b)
= Creosote-Tarbush Cover Type (Plumb 1988)
? Creosotebush-Tarbush (Leopold and Krausman 1988)
= Creosotebush-Tarbush/Sparse Undergrowth PA (Muldavin et al. 2000b) [(Larrea tridentata-Flourensia cernua/Sparse; LARTRI-FLOCER/SPARSE)]

Concept Author(s): Muldavin et al. (2000b)

Author of Description: Muldavin et al. (2000b)

Acknowledgements: No Data Available

Version Date: 08-30-12

  • Bourgeron, P. S., and L. D. Engelking, editors. 1994. A preliminary vegetation classification of the western United States. Unpublished report. The Nature Conservancy, Western Heritage Task Force, Boulder, CO. 175 pp. plus appendix.
  • Buffington, L. C., and C. H. Herbel. 1965. Vegetational changes on a semidesert grassland range from 1858 to 1963. Ecological Monographs 35(2):139-164.
  • Diamond, D. D. 1993. Classification of the plant communities of Texas (series level). Unpublished document. Texas Natural Heritage Program, Austin. 25 pp.
  • Dick-Peddie, W. A. 1993. New Mexico vegetation: Past, present, and future. University of New Mexico Press, Albuquerque. 244 pp.
  • Gehlbach, F. R. 1967. Vegetation of the Guadalupe Escarpment, New Mexico-Texas. Ecology 48:404-419.
  • Laurenroth, W. K., D. P. Coffin, T. B. Kirchner, and O. E. Sala. 1994b. The importance of soil water in the recruitment of Bouteloua gracilis in the shortgrass steppe. Ecological Applications 4:741-749.
  • Leopold, B. D., and P. R. Krausman. 1988. Plant associations of the lower desert shrubland in Big Bend National Park, Texas. Contributed paper second symposium on the Resources of the Chihuahuan Desert. Chihuahuan Desert Research Institute, Alpine, TX. 47 pp.
  • Montana, C., B. Cavagnaro, and O. Briones. 1995. Soil water use by co-existing shrubs and grasses in the Southern Chihuahuan Desert, Mexico. Journal of Arid Environments 31:1-13.
  • Muldavin, E., M. P. Moreno, J. Thomson, and P. Mehlhop. 1994b. A vegetation map for White Sands National Monument. Final report prepared for White Sands National Monument: Alamogordo, NM, by New Mexico Natural Heritage Program.
  • Muldavin, E., V. Archer, and P. Neville. 1998a. A vegetation map of the Borderlands Ecosystem Management Area. Final report submitted to USDA Forest Service, Rocky Mountain Experiment Station, Flagstaff, AZ, by the New Mexico Natural Heritage Program, University of New Mexico, Albuquerque, NM. 58 pp.
  • Muldavin, E., Y. Chauvin, and G. Harper. 2000b. The vegetation of White Sands Missile Range, New Mexico: Volume I. Handbook of vegetation communities. Final report to Environmental Directorate, White Sands Missile Range. New Mexico Natural Heritage Program, University of New Mexico, Albuquerque. 195 pp. plus appendices
  • Plumb, G. A. 1988. An algorithmic approach to automated vegetation mapping of Big Bend National Park, Texas. Ph.D. dissertation, University of Kansas, Lawrence. 449 pp.
  • Rzedowski, J. 1981. Vegetaciòn de México. Editorial Limusa, Mexico City, Mexico. 432 pp.
  • Steward, L. H. 1982. Desert grassland communities on Otero Mesa, Otero County, New Mexico. Unpublished thesis, New Mexico State University, Las Cruces.
  • Van Devender, T. R. 1995. Desert grassland history: Changing climates, evolution, biogeography, and community dynamics. Pages 68-99 in: J. A. McClaran and T. R.Van Devender, editors. The Desert Grassland. University of Arizona Press, Tucson.
  • Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.
  • Wood, S., E. T. Bennet, E. Muldavin, and S. Yanoff. 1998. Vegetation classification and map for Fort Bliss, Texas and New Mexico. Final report to the Directorate of Environment, Fort Bliss, TX, by the New Mexico Natural Heritage Program, University of New Mexico, Albuquerque.