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CEGL002914 Cercocarpus montanus / Muhlenbergia montana Shrubland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Alderleaf Mountain-mahogany / Mountain Muhly Shrubland

Colloquial Name: No Data Available

Hierarchy Level:  Association

Type Concept: This association is part of the lower montane-foothills shrubland ecosystem within the eastern slope of the southern Rocky Mountains between 2410 and 2623 m (7900-8600 feet) in elevation. This ecosystem may occur as a mosaic of two or three plant associations often surrounded by grasslands or woodlands. These slopes are typically oriented southerly, between approximately 125° and 190°, although a few ridges are more westerly trending. The slopes are steep, from 7-22%, and are rapidly drained. This shrubland occupies gravelly substrates and rocky sites on the dry, upper steep slopes (25-56%) of hills and ridges. The vegetation is characterized by an open to moderately dense short-shrub layer (<2 m) dominated by Cercocarpus montanus, typically with a lush herbaceous layer dominated by Muhlenbergia montana. Cercocarpus montanus shrubs are scattered on these sites, e.g., the canopies rarely overlap, unlike very dense stands that grow at lower elevations in Colorado and nearby states. Along with Cercocarpus montanus, a few Ribes cereum or Rhus trilobata shrubs occur on most sites. Because this type occupies canopy breaks in foothill and montane woodlands or is occasionally invaded by Pinus ponderosa trees, it is not unusual to have some foliar cover provided by tree canopies. Total vegetation cover for Cercocarpus montanus stands was estimated at from 40-70%, depending on the amount of understory herbaceous growth. Dwarf-shrubs, typically Yucca glauca, Artemisia frigida, Opuntia polyacantha, and young Cercocarpus montanus, are present but often provide less than 5% foliar cover. The herbaceous layer is generally dominated by graminoids, particularly Muhlenbergia montana, Festuca arizonica, and Bouteloua gracilis.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: Some stands of this associations are very similar to ~Cercocarpus montanus / Hesperostipa comata Shrubland (CEGL001092)$$ and may be codominated by Hesperostipa comata. However, Muhlenbergia montana will be absent or low cover in stands of ~Cercocarpus montanus / Hesperostipa comata Shrubland (CEGL001092)$$.

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

Physiognomy and Structure: No Data Available

Floristics: This shrubland association is characterized by an open to moderately dense short-shrub layer (<2 m) dominated by Cercocarpus montanus, typically with a lush herbaceous layer dominated by Muhlenbergia montana. Other shrubs often include a few Ribes cereum or Rhus trilobata on most sites. Because this type occupies breaks in the tree canopy, it is occasionally invaded by Pinus ponderosa trees, and it is not unusual to have some foliar cover provided by tree canopies. The shrub canopies rarely overlap, unlike very dense stands that grow at lower elevations in Colorado and nearby states. Many stands have a relatively sparse shrub layer and can actually be dominated by graminoids, particularly Muhlenbergia montana, with Hesperostipa comata and Bouteloua gracilis often codominant. Total vegetative cover for Cercocarpus montanus stands was estimated at from 40-70%, depending on the amount of understory herbaceous growth. Dwarf-shrubs, typically Yucca glauca, Artemisia frigida, and young Cercocarpus montanus, are present but usually provide less than 5% foliar cover. The herbaceous layer is a mixture of grasses and forbs. Associated species include Achnatherum scribneri, Bouteloua gracilis, Carex geyeri, Elymus albicans (= Elymus lanceolatus ssp. albicans), Festuca arizonica, and the perennial forbs Helianthus pumilus, Heterotheca villosa, Potentilla fissa, and Scutellaria brittonii. Introduced annual grass Bromus tectorum is often present.

Dynamics:  No Data Available

Environmental Description:  This shrubland association is part of the lower montane-foothills shrubland ecosystem found in the Front Range of Colorado, generally occurring between 2155 and 2623 m (7065-8600 feet) in elevation. This association may occur as a mosaic of two or three plant associations often surrounded by grasslands or woodlands. This shrubland occupies gravelly substrates and rocky sites on the dry, upper steep slopes (25-56%) of hills and ridges. These slopes are typically oriented southerly, between approximately 125° and 190°, although a few ridges are more westerly trending. The slopes are steep, from 7-25%, and are rapidly drained. Substrates are typically rocky soils.

Geographic Range: This foothill to lower montane shrubland association occurs on the east slope of the southern Rocky Mountains in Colorado.

Nations: US

States/Provinces:  CO




Confidence Level: Moderate

Confidence Level Comments: No Data Available

Grank: GU

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: = Cercocarpus montanus / Muhlenbergia montana Plant Association (Johnston 1987)

Concept Author(s): Western Ecology Group

Author of Description: K.A. Schulz

Acknowledgements: No Data Available

Version Date: 08-04-05

  • CNHP Ecology Team [Colorado Natural Heritage Program Ecology Team]. 2001. A classification of the native vegetation of Colorado. Colorado Natural Heritage Program, Colorado State University, Fort Collins.
  • CNHP [Colorado Natural Heritage Program]. 2006-2017. Tracked natural plant communities. Colorado Natural Heritage Program, Colorado State University, Fort Collins. [https://cnhp.colostate.edu/ourdata/trackinglist/plant_communities/]
  • Johnston, B. C. 1987. Plant associations of Region Two: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas. R2-ECOL-87-2. USDA Forest Service, Rocky Mountain Region. Lakewood, CO. 429 pp.
  • Neely, B., P. Comer, C. Moritz, M. Lammerts, R. Rondeau, C. Prague, G. Bell, H. Copeland, J. Humke, S. Spakeman, T. Schulz, D. Theobald, and L. Valutis. 2001. Southern Rocky Mountains: An ecoregional assessment and conservation blueprint. Prepared by The Nature Conservancy with support from the U.S. Forest Service, Rocky Mountain Region, Colorado Division of Wildlife, and Bureau of Land Management.
  • Owns, T., project coordinator, et al. 2004. U.S. Geological Survey and National Park Service Vegetation Mapping Program: Florissant Fossil Beds National Monument. U.S. Geological Survey and National Park Service. 390 pp.
  • Radloff, D. L. 1983. Wildland classification with multivariate analysis and remote sensing techniques. Unpublished dissertation. Colorado State University, Fort Collins. 106 pp.
  • Salas, D. E., J. Stevens, K. Schulz, M. Artmann, B. Friesen, S. Blauer, E. W. Schweiger, and A. Valdez. 2010b. Vegetation classification and mapping project report: Great Sand Dunes National Park and Preserve. Natural Resource Report NPS/ROMN/NRR--2010/179. National Park Service, Fort Collins, CO.
  • Salas, D., J. Stevens, and K. Schulz. 2005. USGS-NPS Vegetation Mapping Program: Rocky Mountain National Park, Colorado. Technical Memorandum No. 8260-05-02. USDI Bureau of Reclamation, Denver, CO. 161 pp. plus Appendices A-L (733 pp.).
  • Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.