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CEGL000357 Picea engelmannii / Caltha leptosepala Swamp Forest
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Engelmann Spruce / White Marsh-marigold Swamp Forest
Colloquial Name: No Data Available
Hierarchy Level: Association
Type Concept: This forest association is found east of the Continental Divide in Wyoming on cold and subirrigated sites along streambanks and terraces between 2499 and 2896 m (8200-9500 feet) elevation. It also occurs in north-central Wyoming in the Big Horn Mountains and in the southern and western portions of the Uinta Mountains of Utah between 3048 and 3322 m (10,000-10,900 feet) elevation. Soils are noncalcareous and derived primarily from granitic alluvium. Picea engelmannii dominates both late-successional and early-seral communities; Abies lasiocarpa is occasionally present but is stunted and unhealthy. Minor seral components are Pinus contorta and Pinus albicaulis. The shrub layer is not diverse, but common shrubs present include Vaccinium cespitosum and Vaccinium scoparium. The herbaceous undergrowth is floristically rich, with either Caltha leptosepala or Trollius laxus having at least 5% cover. A number of other wet-site forbs and graminoids are present to abundant, including Arnica spp., Calamagrostis canadensis, Deschampsia cespitosa, Mitella pentandra, Parnassia fimbriata, Saxifraga odontoloma, Senecio triangularis, and species of Carex or Juncus. On drier sites, Antennaria microphylla, Danthonia intermedia, Poa nervosa, and Trisetum spicatum are present.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: Steele et al. (1981) describe a similar habitat type Abies lasiocarpa [Picea engelmannii]/ Caltha biflora from central Idaho, which is represented in the USNVC by ~Abies lasiocarpa / Caltha leptosepala ssp. howellii Swamp Forest (CEGL000302)$$.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: Picea engelmannii is the dominant species in late-successional stands. Although Abies lasiocarpa may be present, individual trees are normally stunted and only occupy drier microsites. Pinus contorta is a major seral associate. The only common shrubs are Vaccinium cespitosum and Vaccinium scoparium. The undergrowth is predominately herbaceous with Caltha leptosepala, Arnica spp., Pedicularis bracteosa, Pedicularis groenlandica, Polygonum bistortoides, Potentilla spp., Sibbaldia procumbens, Trifolium spp., Carex heteroneura var. epapillosa, Carex scirpoidea, Deschampsia cespitosa, Luzula spicata, and Phleum alpinum being the commonly occurring moist- or cold-site species. A number of other wet-site forbs and graminoids are present to abundant, including Calamagrostis canadensis, Mitella pentandra, Parnassia fimbriata, Saxifraga odontoloma (= Saxifraga arguta), Senecio triangularis, and species of Carex or Juncus. Other species sometimes present are Veronica wormskjoldii, Festuca ovina, and Poa alpina. On drier sites, Antennaria microphylla, Erigeron peregrinus, Danthonia intermedia, Poa nervosa, and Trisetum spicatum are found.
Dynamics: Crane (1982) places this association into fire group sixteen, which includes very moist spruce and subalpine fir habitat types. Fire appears to play a relatively minor role on these types. Lodgepole pine''s presence indicates that they must burn occasionally, probably during a severe wind-driven fire during a particularly dry year. If they do burn, recovery to a seral forest should be rapid. Low surface fires could occur during years when the site was too moist to burn severely but when a severe fire was carried across adjacent drier sites.
Along a general successional path, an herb stage is followed by the sprouting of shrubs along with seedlings and saplings of the seral stand. A fire at this point, though unlikely, would return the site to the herb stage. In a pole-sized stand, fire is also unlikely because of the moisture and lowered fuels. A low surface fire could open the stand and expose mineral soil for regeneration. The mature forest favors a severe, stand-replacement fire under dry conditions.
In the absence of fire, a climax forest of Engelmann spruce could develop with little lodgepole pine left. This stage is, however, unlikely as springtime flooding is a common disturbance that can create openings and expose sites.
Along a general successional path, an herb stage is followed by the sprouting of shrubs along with seedlings and saplings of the seral stand. A fire at this point, though unlikely, would return the site to the herb stage. In a pole-sized stand, fire is also unlikely because of the moisture and lowered fuels. A low surface fire could open the stand and expose mineral soil for regeneration. The mature forest favors a severe, stand-replacement fire under dry conditions.
In the absence of fire, a climax forest of Engelmann spruce could develop with little lodgepole pine left. This stage is, however, unlikely as springtime flooding is a common disturbance that can create openings and expose sites.
Environmental Description: This association is found from 3050 to 3320 m (8200-10,900 feet) elevation, at the upper end of regional subalpine zones. It is found on gentle slopes and subirrigated positions, often with seasonably high water tables. The soils for this type are moist and have loamy to clayey textures and gravel. Parent materials include granitics, quartzite, and sandstone. There is some surface rock, but little or no bare soil. Litter averages 3.4 cm (1.34 inches) in depth.
Geographic Range: This forest association is found east of the Continental Divide in Wyoming (Wind River, Absaroka, and Beartooth ranges) on cold sites along streambanks and terraces between 2499 and 2896 m (8200-9500 feet) elevation. It also occurs in north-central Wyoming in the Big Horn Mountains and in the southern and western portions of the Uinta Mountains of Utah between 3048 and 3322 m (10,000-10,900 feet) elevation.
Nations: US
States/Provinces: CO, ID?, MT, UT, WY
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.683818
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G3?
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 1 Forest & Woodland Class | C01 | 1 |
Subclass | 1.B Temperate & Boreal Forest & Woodland Subclass | S15 | 1.B |
Formation | 1.B.3 Temperate Flooded & Swamp Forest Formation | F026 | 1.B.3 |
Division | 1.B.3.Nc Rocky Mountain-Great Basin Montane Flooded & Swamp Forest Division | D195 | 1.B.3.Nc |
Macrogroup | 1.B.3.Nc.1 Engelmann Spruce - Narrowleaf Cottonwood / Red-osier Dogwood Riparian & Swamp Forest Macrogroup | M034 | 1.B.3.Nc.1 |
Group | 1.B.3.Nc.1.a Engelmann Spruce - Blue Spruce - Narrowleaf Cottonwood Riparian & Swamp Forest Group | G506 | 1.B.3.Nc.1.a |
Alliance | A3757 Subalpine Fir - Engelmann Spruce Swamp Forest Alliance | A3757 | 1.B.3.Nc.1.a |
Association | CEGL000357 Engelmann Spruce / White Marsh-marigold Swamp Forest | CEGL000357 | 1.B.3.Nc.1.a |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = Picea engelmannii / Caltha leptosepala Habitat Type (Steele et al. 1983)
= Picea engelmannii / Caltha leptosepala Plant Association (Johnston 1987)
= Picea engelmannii / Caltha leptosepala Habitat Type (Mauk and Henderson 1984) [This habitat type is found in the southern and western Uinta Mountains of Utah.]
= Picea engelmannii / Caltha leptosepala Plant Association (Johnston 1987)
= Picea engelmannii / Caltha leptosepala Habitat Type (Mauk and Henderson 1984) [This habitat type is found in the southern and western Uinta Mountains of Utah.]
- 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.
- 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/]
- Crane, M. F. 1982. Fire ecology of Rocky Mountain Region forest habitat types. USDA Forest Service final report. 272 pp.
- IDCDC [Idaho Conservation Data Center]. 2005. Wetland and riparian plant associations in Idaho. Idaho Conservation Data Center, Idaho Department of Fish and Game, Boise. [http://fishandgame.idaho.gov/tech/CDC/ecology/wetland_riparian_assoc.cfm] (accessed 14 June 2005).
- 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.
- Jones, G., and S. Ogle. 2000. Characterization abstracts for vegetation types on the Bighorn, Medicine Bow, and Shoshone national forests. Prepared for USDA Forest Service, Region 2 by the Wyoming Natural Diversity Database, University of Wyoming.
- MTNHP [Montana Natural Heritage Program]. 2002b. List of ecological communities for Montana. Montana Natural Heritage Program, Montana State Library, Helena, MT.
- Mauk, R. L., and J. A. Henderson. 1984. Coniferous forest habitat types of northern Utah. General Technical Report INT-170. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT. 89 pp.
- Steele, R., S. V. Cooper, D. M. Ondov, D. W. Roberts, and R. D. Pfister. 1983. Forest habitat types of eastern Idaho - western Wyoming. General Technical Report INT-144. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT. 122 pp.
- WNDD [Wyoming Natural Diversity Database]. No date. Unpublished data on file. Wyoming Natural Diversity Database, University of Wyoming, Laramie, WY.
- Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.