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CEGL002657 Salix monticola / Carex utriculata Wet Shrubland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Park Willow / Northwest Territory Sedge Wet Shrubland

Colloquial Name: No Data Available

Hierarchy Level:  Association

Type Concept: This plant association is found throughout the southern Rocky Mountains of Colorado. It occurs along wet banks and terraces of low-gradient, subalpine streams at 2500-3100 m (8300-10,240 feet) elevation in broad valley bottoms, commonly near beaver ponds. Soils are heavy clay loams, sandy clay loams, and heavy silty clays, often with significant organic matter. This plant association is a tall (1.5-2.5 m [5-8 feet]), deciduous shrubland with an open canopy of willows and a thick understory of grasses and sedges. Willows establish on higher hummocks, while Carex utriculata establishes at the water margins and in wet swales between willow hummocks. The willow canopy is dominated by Salix monticola (10-80% cover), although other species may include Salix geyeriana, Salix brachycarpa, Salix drummondiana, Salix ligulifolia, and Salix boothii. The undergrowth is dominated by patches of Carex utriculata, but Carex aquatilis, Deschampsia cespitosa, and Calamagrostis canadensis are often present as well. Total forb cover is generally <10% and may include Cardamine cordifolia, Mertensia ciliata, and Heracleum maximum.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: Classification is based on 13 quantitative plots in Colorado, the only known area of occurrence. In the understory Carex utriculata is either the clear dominant or is most consistently present throughout the stand. This distinguishes this association from ~Salix monticola / Carex aquatilis Wet Shrubland (CEGL002656)$$ and ~Salix monticola / Calamagrostis canadensis Wet Shrubland (CEGL001222)$$.

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

Physiognomy and Structure: No Data Available

Floristics: This plant association is a tall (1.5-2.5 m [5-8 feet]), deciduous shrubland with an open canopy of willows and a thick understory of grasses and sedges. The willow canopy is dominated by Salix monticola (10-80% cover), although other species (with percent cover) may include Salix geyeriana (4-40%), Salix brachycarpa (2-28%), Salix drummondiana (1-20%), Salix ligulifolia (= Salix eriocephala var. ligulifolia) (1-11%), and Salix boothii (1%). Betula occidentalis and Dasiphora fruticosa ssp. floribunda can reach up to 10% cover. Ribes spp. are often present in low abundance. The undergrowth is dominated by patches of Carex utriculata (1-44% cover), but Carex aquatilis (1-11% cover), Deschampsia cespitosa, and Calamagrostis canadensis are often present as well. Total forb cover is generally <10% and may include Agrostis scabra, Caltha leptosepala, Cardamine cordifolia, Geum macrophyllum, Mertensia ciliata, and Heracleum maximum (Kittel et al. 1997b, Carsey et al. 2003a, 2003b).

Dynamics:  Salix monticola appears to be less tolerant of browsing pressure than other tall montane willow species. It responds to heavy browsing pressure in the same way that Salix geyeriana does; it forms the classic "mushroom" shape with over browsing by deer and cattle (Hansen et al. 1995). Carex species can be heavily grazed by livestock in narrow riparian areas in mid-elevation rangelands. Improper grazing by livestock in this plant association can dry sites, increase non-native cover, and reduce the vigor of willow root structure. The wet and often saturated soils of this plant association are also vulnerable to compaction by livestock and heavy equipment. In order to maintain productivity and vigor of the plants and prevent damage to the soils, livestock grazing should be deferred until soils dry (Hansen et al. 1995).

Changes in the physical environment, brought on by flooding or other disturbance, can initiate successional shifts in species composition. Sediment deposition on the floodplain raises the surface higher above the water table. As aggradation, or build up, of the floodplain proceeds, the site becomes drier and the dominant graminoid understory changes. Thus Carex aquatilis-dominated stands (regardless of any overstory canopy) may shift toward Calamagrostis canadensis-dominated stands.

Environmental Description:  This association occurs along wet banks and terraces of low-gradient, subalpine streams at 2500-3100 m (8300-10,240 feet) elevation in broad valley bottoms, commonly near beaver ponds. Soils are heavy (clay loam, sandy clay loam, heavy silty clay textures), often with significant organic matter. Willows establish on higher hummocks, while Carex utriculata establishes at the water margins and in wet swales between willow hummocks. It can form very wide and thick shrublands in broad valley bottoms, or it can occur as a narrow strip of linear vegetation along smaller streams in narrow, constricted tributaries (Kittel et al. 1997b, Carsey et al. 2003a, 2003b).

Geographic Range: This plant association is found throughout the southern Rocky Mountains of Colorado.

Nations: US

States/Provinces:  CO




Confidence Level: Moderate

Confidence Level Comments: No Data Available

Grank: G3

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: < Salix drummondiana - Salix monticola / Calamagrostis canadensis - Carex utriculata (Baker 1989b)
>< Salix monticola / Calamagrostis canadensis Plant Association (Cooper and Cottrell 1990) [Some stands included in this type were dominated by Carex utriculata.]
= Salix monticola / Carex rostrata Habitat Type (Hansen et al. 1995)
= Salix monticola / Carex utriculata Plant Association (Kittel et al. 1999b)
= Salix monticola / Carex utriculata Shrubland (Carsey et al. 2003a)
= Salix monticola / Carex utriculata Shrubland (Carsey et al. 2003b)

Concept Author(s): R.J. Rondeau

Author of Description: R.J. Rondeau, G. Kittel and K.A. Schulz

Acknowledgements: No Data Available

Version Date: 07-25-05

  • Baker, W. L. 1989b. Classification of the riparian vegetation of the montane and subalpine zones in western Colorado. Great Basin Naturalist 49(2):214-228.
  • 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/]
  • Carsey, K., D. Cooper, K. Decker, D. Culver, and G. Kittel. 2003b. Statewide wetlands classification and characterization: Wetland plant associations of Colorado. Prepared for Colorado Department of Natural Resources, Denver, by Colorado Natural Heritage Program, College of Natural Resources, Colorado State University, Fort Collins. 79 pp. [http://www.cnhp.colostate.edu/documents/2003/wetland_classification_final_report_2003.pdf]
  • Carsey, K., G. Kittel, K. Decker, D. J. Cooper, and D. Culver. 2003a. Field guide to the wetland and riparian plant associations of Colorado. Colorado Natural Heritage Program, Fort Collins, CO.
  • Cooper, D. J., and T. R. Cottrell. 1990. Classification of riparian vegetation in the northern Colorado Front Range. Unpublished report prepared for The Nature Conservancy, Colorado Field Office, Boulder. 115 pp.
  • Hansen, P. L., R. D. Pfister, K. Boggs, B. J. Cook, J. Joy, and D. K. Hinckley. 1995. Classification and management of Montana''s riparian and wetland sites. Miscellaneous Publication No. 54. Montana Forest and Conservation Experiment Station, School of Forestry, University of Montana. 646 pp. plus posters.
  • Kittel, G., E. Van Wie, M. Damm, R. Rondeau, S. Kettler, A. McMullen, and J. Sanderson. 1999b. A classification of riparian and wetland plant associations of Colorado: A user''s guide to the classification project. Colorado Natural Heritage Program, Colorado State University, Fort Collins CO. 70 pp. plus appendices.
  • Kittel, G., E. Van Wie, M. Damm, R. Rondeau, S. Kettler, and J. Sanderson. 1999a. A classification of the riparian plant associations of the Rio Grande and Closed Basin watersheds, Colorado. Unpublished report prepared by the Colorado Natural Heritage Program, Colorado State University, Fort Collins.
  • Kittel, G., E. Van Wie, and M. Damm. 1997b. Populus deltoides ssp. monilifera / Symphoricarpos occidentalis Community Characterization Abstract-Subnational Basic, draft March 12, 1997. Colorado Natural Heritage Program, Fort Collins, CO.
  • Kittel, G., R. Rondeau, N. Lederer, and D. Randolph. 1994. A classification of the riparian vegetation of the White and Colorado River basins, Colorado. Final report submitted to Colorado Department of Natural Resources and the Environmental Protection Agency. Colorado Natural Heritage Program, Boulder. 166 pp.
  • Kittel, G., R. Rondeau, and S. Kettler. 1995. A classification of the riparian vegetation of the Gunnison River Basin, Colorado. Submitted to Colorado Department of Natural Resources and the Environmental Protection Agency. Prepared by Colorado Natural Heritage Program, Fort Collins. 114 pp.
  • 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.
  • Richard, C., G. Kittel, and S. Kettler. 1996. A classification of the riparian vegetation of the San Juan National Forest. Draft 1 report. Colorado Natural Heritage Program, Colorado State University, Fort Collins.
  • 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.