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CEGL001282 Atriplex canescens - Artemisia tridentata Shrubland
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Fourwing Saltbush - Big Sagebrush Shrubland
Colloquial Name: No Data Available
Hierarchy Level: Association
Type Concept: This shrubland is found on the western slope of the Colorado Rocky Mountains, Colorado Plateau, Great Basin, and Mojave Desert. The vegetation is characterized by a sparse to moderately dense (10-35% cover) short-shrub layer that is codominated by Atriplex canescens and Artemisia tridentata. On some sites, Pinus edulis and/or Juniperus osteosperma canopy trees provide sparse cover. Chrysothamnus viscidiflorus, Ephedra nevadensis, Ericameria nauseosa, Gutierrezia sarothrae, Gutierrezia microcephala, Sarcobatus vermiculatus, and Suaeda moquinii may be present with low cover on more saline sites. The sparse to moderate herbaceous layer (10-20% cover) is dominated by graminoids with scattered forbs. Achnatherum hymenoides, Bouteloua gracilis, Elymus elymoides, Muhlenbergia asperifolia, and Pascopyrum smithii are common grasses. Forbs have low and varied cover and may include Cirsium neomexicanum, Eriogonum inflatum, or Sphaeralcea coccinea. Introduced species are common in disturbed stands. Elevation ranges from 1160-2100 m (3800-6900 feet). Stands occur on level plains, valley bottoms, alluvial flats, stream terraces, low and midslopes. Slopes are typically less than 25%, but this shrubland has been documented on steep slopes as well. It occurs on all aspects. Substrates are well-drained, typically fine-textured soils (silty loam and clay) but may include coarser-textured soils (loamy sand).
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: This association is characterized by a sparse to moderately dense (10-35% cover) short-shrub layer (1-2 m tall) that is codominated by Atriplex canescens and Artemisia tridentata. On some sites, Pinus edulis and/or Juniperus osteosperma canopy trees provide sparse cover. Associated shrubs include Chrysothamnus viscidiflorus, Ephedra viridis, Ephedra nevadensis, Eriogonum corymbosum, Ericameria nauseosa, Gutierrezia sarothrae, Gutierrezia microcephala, Krascheninnikovia lanata, Lycium spp., Opuntia spp., and Salix gooddingii (Warren et al. 1982, Roberts et al. 1992). Sarcobatus vermiculatus and Suaeda moquinii may be present with low cover on more saline sites. The sparse to moderately dense (10-20% cover) herbaceous layer is dominated by graminoids with scattered forbs. Achnatherum hymenoides, Bouteloua gracilis, Elymus elymoides, Leymus salinus, Muhlenbergia asperifolia, Pleuraphis jamesii, Pascopyrum smithii, and Sporobolus cryptandrus are common grasses. Forbs may include Abronia fragrans, Cirsium neomexicanum, Eriogonum inflatum, Eriogonum racemosum, Heliomeris longifolia (= Viguiera longifolia), Lappula occidentalis, Machaeranthera canescens, Mentzelia multiflora, Oenothera caespitosa, Penstemon spp., Rumex hymenosepalus, or Sphaeralcea coccinea. Introduced species such as Agropyron cristatum, Arctium minus, Bromus rubens, Bromus tectorum, Carduus nutans, Chenopodium album, Cirsium arvense, Convolvulus arvensis, Descurainia sophia, Erodium cicutarium, Lactuca serriola, Lappula occidentalis, Medicago sativa, Salsola tragus, and Tragopogon dubius are common in disturbed stands. Cryptogams are generally sparse but one sampled plot had 25% cover.
Dynamics: Atriplex canescens is tolerant of fire and generally sprouts vigorously from the rootcrown after burning (Wright 1980). It often recovers fully within 2 or 3 years after a burn (Wright 1980). However, Artemisia tridentata shrubs are readily killed by fire and do not resprout (Wright et al. 1979). Artemisia tridentata will re-establish relatively quickly (about 10-20 years) if a seed source is nearby (Bunting 1987). If fire-return intervals are more frequent than 10 years, then Artemisia tridentata has difficulty recovering (Bunting 1987, Everett 1987). This community is an interesting combination of a species with different tolerances to soil alkalinity and salinity. Although Artemisia tridentata occurs on a variety of substrates, it is intolerant of strongly alkaline and saline soils (Howard 1999, 2003), whereas Atriplex canescens, which also occurs on a wide variety of substrates, can tolerates saline, alkaline, boron, and gypsum soils (Howard 2003). This frequently results in relatively sharp boundaries between fourwing saltbush and big sagebrush communities, although each species may occur as associates for the other. More research is needed to understand the dynamics of this mixed shrub community.
Environmental Description: Elevation ranges from 1160-2100 m (3800-6900 feet). Stands occur on level plains, canyon floors, valley bottoms, alluvial flats, stream terraces, benches, low and midslopes. Slopes are typically less than 25%, but this shrubland has been documented on steep slopes. It occurs on all aspects, but northwest-, east- and southeast-facing slopes are common. Substrates are well-drained, typically fine-textured soils (silty loam and clay) but may include coarser-textured soils (loamy sand). Some stands may be subject to periodic flooding. Evidence of erosion, such as rills and gullies, is common (Warren et al. 1982).
Geographic Range: This shrubland is found on the western slope of the Colorado Rocky Mountains, Colorado Plateau, Great Basin, and Mojave Desert.
Nations: US
States/Provinces: AZ, CA?, CO, NV, UT
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.686956
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G4
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 3 Desert & Semi-Desert Class | C03 | 3 |
Subclass | 3.B Cool Semi-Desert Scrub & Grassland Subclass | S11 | 3.B |
Formation | 3.B.1 Cool Semi-Desert Scrub & Grassland Formation | F033 | 3.B.1 |
Division | 3.B.1.Ne Western North American Cool Semi-Desert Scrub & Grassland Division | D040 | 3.B.1.Ne |
Macrogroup | 3.B.1.Ne.5 Shadscale Saltbush - Fourwing Saltbush - Mat Saltbush Great Basin Scrub Macrogroup | M093 | 3.B.1.Ne.5 |
Group | 3.B.1.Ne.5.b Shadscale Saltbush - Fourwing Saltbush - Spiny Hopsage Scrub Group | G300 | 3.B.1.Ne.5.b |
Alliance | A0869 Fourwing Saltbush Scrub Alliance | A0869 | 3.B.1.Ne.5.b |
Association | CEGL001282 Fourwing Saltbush - Big Sagebrush Shrubland | CEGL001282 | 3.B.1.Ne.5.b |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = 152.1721 Atriplex canescens - Artemisia tridentata - Gutierrezia sarothrae (Warren et al. 1982)
= Artemisia tridentata / Atriplex canescens Habitat Type (Roberts et al. 1992)
= Artemisia tridentata / Atriplex canescens Habitat Type (Roberts et al. 1992)
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- Everett, R. L. 1987. Plant response to fire in the pinyon-juniper zone. Pages 152-157 in R. L. Everett, compiler. Proceedings pinyon-juniper conference: 1986 January 13-16, Reno, NV. General Technical Report INT-215. USDA Forest Service, Intermountain Research Station, Ogden, UT.
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- Howard, J. L. 2003a. Atriplex canescens. In: Fire Effects Information System [Online]. USDA Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). [http://www.fs.fed.us/database/feis/] (accessed 13 July 2007).
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