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CEGL005882 Larix occidentalis / Vaccinium cespitosum Forest
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Western Larch / Dwarf Bilberry Forest
Colloquial Name: No Data Available
Hierarchy Level: Association
Type Concept: This small- to large-patch minor forested type occurs throughout the northern Rocky Mountains. Its presence is strongly associated with well-drained sites in frosty basins or benchlands where cold air accumulates. It is found at moderate elevations between 915 to 1220 m (3000-4000 feet) in the western portion of its distribution but occurs as high as 1525 m (5000 feet) on the Flathead and Kootenai national forests, and yet further to the east it may be found to 2195 m (7200 feet) in basins along the Continental Divide. These sites are postulated to experience frequent summer frost coupled with warm daily maximum temperatures; this factor combination is thought to be limiting to climax conifer species, which establish and grow slowly on these sites. Surface soils are mostly derived from alluvial and to lesser degree colluvial deposits, both gravelly and non-gravelly sandy loams to silts with acidic reaction (pH averaged 5.0 in Montana for comparable type). Sites with the above suite of characteristics are generally dominated by Pinus contorta in the overstory, but occasionally Larix occidentalis becomes abundantly established, the unique result of a plentiful local Larix cone crop and a stand-replacing disturbance (wildfire) and a non-serotinous local population of Pinus contorta. Pseudotsuga menziesii and Pinus contorta are present as a minor component of open canopies dominated by Larix occidentalis; Abies lasiocarpa and Picea engelmannii are present as depauperate specimens in the reproductive layers. Though short shrubs may be represented and even exhibit high constancy (e.g., Amelanchier alnifolia, Lonicera utahensis, Spiraea betulifolia, Shepherdia canadensis, Juniperus communis), it is the dwarf-shrub layer that dominates. Cover of the two indicators of the type, Vaccinium cespitosum and Arctostaphylos uva-ursi, varies markedly, from a few percent to nearly a continuous layer. Other dwarf-shrubs with a consistent presence and occasional abundance are Linnaea borealis, Mahonia repens, Vaccinium scoparium, and Vaccinium myrtillus. Calamagrostis rubescens consistently dominates the graminoid component, and frequently it fills the interstices between dwarf-shrubs to create a virtually unbroken layer. Carex geyeri and Carex concinnoides are also moderately constant within the type. Forbs are usually a negligible component with only Arnica cordifolia, Orthilia secunda, Hieracium albiflorum, and Maianthemum racemosum exhibiting moderate to high constancy.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: Differences in site parameters are probably insignificant among Larix occidentalis / Vaccinium cespitosum, Pinus contorta / Vaccinium cespitosum, and Pseudotsuga / Vaccinium cespitosum communities; these communities owe their canopy differences to happenstance; tree layer dominance accrues to whichever species has greater effective proximity (in a statistical sense) to an appropriate disturbed site and an abundant cone crop upwind of the site (at the time of and following disturbance). The cover values at which Vaccinium cespitosum and Arctostaphylos uva-ursi are recognized as indicators ranges from merely present and not confined to microsites (Pfister et al. 1977, Williams and Lillybridge 1983) to greater than 5% (Lillybridge et al. 1995, Williams et al. 1995), though in most keys Vaccinium cespitosum is generally accorded greater indicator potential than Arctostaphylos uva-ursi, being recognized as indicative at lower cover values.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: Sites having the above suite of abiotic characteristics generally exhibit an overstory dominated by Pinus contorta, but occasionally Larix occidentalis becomes abundantly established. Its dominance results from the unique conjunction of a stand-replacing disturbance (wildfire), a plentiful local Larix cone crop and a non-serotinous local population of Pinus contorta (which assures that Pinus will not prolifically seed into the disturbed area). Pseudotsuga menziesii and Pinus contorta are present as a minor component of open canopies dominated by Larix occidentalis; Abies lasiocarpa and Picea engelmannii are present as depauperate specimens in the reproductive layers. Though short shrubs may be represented and even exhibit high constancy (e.g., Amelanchier alnifolia, Lonicera utahensis, Spiraea betulifolia, Shepherdia canadensis, Juniperus communis), it is the dwarf-shrub layer that dominates. Cover of the two indicators of the type, Vaccinium cespitosum and Arctostaphylos uva-ursi, varies markedly, from a few percent to nearly a continuous layer. Other dwarf-shrubs with a consistent presence and occasional abundance are Linnaea borealis, Mahonia repens, Vaccinium scoparium, and Vaccinium myrtillus. Calamagrostis rubescens consistently dominates the graminoid component, and frequently it fills the interstices between dwarf-shrubs to create a virtually unbroken layer. Carex geyeri and Carex concinnoides are also moderately constant within the type. Forbs are usually a negligible component with only Arnica cordifolia, Fragaria spp., Orthilia secunda (= Pyrola secunda), Lupinus sericeus or Lupinus argenteus (depending on locality), Hieracium albiflorum, and Maianthemum racemosum exhibiting moderate to high constancy and a combined cover seldom exceeding 10%.
Dynamics: This association is generated by stand-replacing fire, the fire-return interval for which is speculated to be on the order of 80 to 200 years. These sites may be maintained in a seral status for hundreds of years due to the fact that Larix occidentalis is a long-lived species and the understory is often dominated by Pseudotsuga, which will grow into the upper canopy. The potential dominants Abies lasiocarpa, Picea engelmannii, or Abies grandis are slow to establish on these sites and grow slowly presenting the distinct probability, given the fire-return intervals for this type, that the climax (long-term stable) condition is never realized.
Environmental Description: This small- to large-patch minor forested type occurs throughout the northern Rocky Mountains. Its presence is strongly associated with well-drained sites in frosty basins or benchlands where cold air accumulates. It is found at moderate elevations between 915 to 1220 m (3000-4000 feet) in the western portion of its distribution but occurs as high as 1525 m (5000 feet) on the Flathead and Kootenai national forests, and yet further to the east it may be found to 2195 m (7200 feet) in basins along the Continental Divide. These sites are postulated to experience frequent summer frost coupled with warm daily maximum temperatures; this factor combination is thought to be limiting to climax conifer species, which establish and grow slowly on these sites. Surface soils are mostly derived from alluvial and to lesser degree colluvial deposits, both gravelly and non-gravelly sandy loams to silts with acidic reaction (pH averaged 5.0 in Montana for comparable type).
Geographic Range: This community occurs from the Idaho Batholith (Payette National Forest) northward in Idaho, throughout northwestern Montana eastward to the Continental Divide and northeastern Washington as far west as the eastern slopes of the Cascades. It is not reported from Canada but would be expected in southern British Columbia (but not Alberta as Larix occidentalis does not extend, except as scattered individuals, east of the Continental Divide).
Nations: CA?,US
States/Provinces: ID, MT, WA
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.728657
Confidence Level: Low
Confidence Level Comments: No Data Available
Grank: GNR
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.2 Cool Temperate Forest & Woodland Formation | F008 | 1.B.2 |
Division | 1.B.2.Nb Rocky Mountain Forest & Woodland Division | D194 | 1.B.2.Nb |
Macrogroup | 1.B.2.Nb.3 Western Hemlock - Grand Fir - Western Larch Mesic Lower Montane Forest Macrogroup | M500 | 1.B.2.Nb.3 |
Group | 1.B.2.Nb.3.a Grand Fir - Douglas-fir - Western Larch Central Rocky Mountain Forest Group | G211 | 1.B.2.Nb.3.a |
Alliance | A0275 Western Larch Central Rocky Mountain Forest Alliance | A0275 | 1.B.2.Nb.3.a |
Association | CEGL005882 Western Larch / Dwarf Bilberry Forest | CEGL005882 | 1.B.2.Nb.3.a |
Concept Lineage: This association and 3 others replace the placeholder.
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: >< Abies grandis / Vaccinium caespitosum Habitat Type (Steele et al. 1981)
>< Abies grandis / Vaccinium caespitosum Plant Association (Williams et al. 1995)
>< Abies lasiocarpa / Vaccinium caespitosum (Lillybridge et al. 1995) [ABLA2/VACA CES422]
>< Abies lasiocarpa / Vaccinium caespitosum Plant Association (Williams et al. 1995)
>< Abies lasiocarpa / Vaccinium cespitosum Habitat Type (Pfister et al. 1977)
>< Abies lasiocarpa / Vaccinium cespitosum Habitat Type (Cooper et al. 1987)
>< Abies lasiocarpa / Vaccinium spp. Plant Association (Williams and Lillybridge 1983)
>< Larix occidentalis - Pseudotsuga menziesii (Pinus contorta) / Shepherdia canadensis - Spiraea betulifolia / Calamagrostis rubescens (Leavell 2000)
>< Larix occidentalis - Pseudotsuga menziesii (Pinus contorta) / Spiraea betulifolia - Amelanchier alnifolia / Calamagrostis rubescens (Leavell 2000)
= Larix occidentalis / Vaccinium caespitosum Forest (Hop et al. 2007)
>< Abies grandis / Vaccinium caespitosum Plant Association (Williams et al. 1995)
>< Abies lasiocarpa / Vaccinium caespitosum (Lillybridge et al. 1995) [ABLA2/VACA CES422]
>< Abies lasiocarpa / Vaccinium caespitosum Plant Association (Williams et al. 1995)
>< Abies lasiocarpa / Vaccinium cespitosum Habitat Type (Pfister et al. 1977)
>< Abies lasiocarpa / Vaccinium cespitosum Habitat Type (Cooper et al. 1987)
>< Abies lasiocarpa / Vaccinium spp. Plant Association (Williams and Lillybridge 1983)
>< Larix occidentalis - Pseudotsuga menziesii (Pinus contorta) / Shepherdia canadensis - Spiraea betulifolia / Calamagrostis rubescens (Leavell 2000)
>< Larix occidentalis - Pseudotsuga menziesii (Pinus contorta) / Spiraea betulifolia - Amelanchier alnifolia / Calamagrostis rubescens (Leavell 2000)
= Larix occidentalis / Vaccinium caespitosum Forest (Hop et al. 2007)
- Cooper, S. V., K. E. Neiman, R. Steele, and D. W. Roberts. 1987. Forest habitat types of northern Idaho: A second approximation. General Technical Report INT-236.USDA Forest Service, Intermountain Research Station, Ogden, UT. 135 pp. [reprinted in 1991]
- Hop, K., M. Reid, J. Dieck, S. Lubinski, and S. Cooper. 2007. U.S. Geological Survey-National Park Service Vegetation Mapping Program: Waterton-Glacier International Peace Park. U.S. Geological Survey, Upper Midwest Environmental Sciences Center, La Crosse, WI. 131 pp. plus Appendices A-L.
- Leavell, D. 2000. Vegetation and process of the Kootenai National Forest. Ph.D. dissertation, University of Montana, Missoula. 508 pp.
- Lillybridge, T. R., B. L. Kovalchik, C. K. Williams, and B. G. Smith. 1995. Field guide for forested plant associations of the Wenatchee National Forest. General Technical Report PNW-GTR-359. USDA Forest Service, Pacific Northwest Research Station, Portland, OR. 335 pp.
- Pfister, R. D., B. L. Kovalchik, S. F. Arno, and R. C. Presby. 1977. Forest habitat types of Montana. General Technical Report INT-34. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT. 174 pp.
- Reid, M. S., S. V. Cooper, and G. Kittel. 2004. Vegetation classification of Waterton-Glacier International Peace Park. Final report for USGS-NPS Vegetation Mapping Program, International Peace Park Mapping Project. NatureServe, Arlington VA.
- Steele, R., R. D. Pfister, R. A. Ryker, and J. A. Kittams. 1981. Forest habitat types of central Idaho. General Technical Report INT-114. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT. 138 pp.
- Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.
- Williams, C. K., B. F. Kelly, B. G. Smith, and T. R. Lillybridge. 1995. Forest plant associations of the Colville National Forest. General Technical Report PNW-GTR-360. USDA Forest Service, Pacific Northwest Region, Portland, OR. 140 pp.
- Williams, C. K., and T. R. Lillybridge. 1983. Forested plant associations of the Okanogan National Forest. R6-Ecol-132b-1983. USDA Forest Service, Pacific Northwest Region, Portland, OR. 140 pp.