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A3398 Pinus ponderosa Southern Rocky Mountain Forest & Woodland Alliance
Type Concept Sentence: This broad and variable alliance represents forest and woodlands of the southern Rocky Mountains with scattered occurrences in adjacent ecoregions dominated by Pinus ponderosa in association with other conifer species.
Common (Translated Scientific) Name: Ponderosa Pine Southern Rocky Mountain Forest & Woodland Alliance
Colloquial Name: Southern Rocky Mountain Ponderosa Pine Forest & Woodland
Hierarchy Level: Alliance
Type Concept: This forest and woodland alliance is widespread in the southwestern mountains occurring primarily in the southern Rocky Mountains, but extending into adjacent ecoregions. It is composed of open to closed forests and woodlands primarily dominated by Pinus ponderosa. Other canopy associates may include Abies concolor, Juniperus scopulorum, Pinus contorta, Pinus edulis, Pinus flexilis, Pinus strobiformis, Populus tremuloides, and Pseudotsuga menziesii. The understory ranges from dense shrub or graminoid layers to barren rock. Common dominant shrubs may include Arctostaphylos patula, Arctostaphylos pungens, Arctostaphylos uva-ursi, Artemisia nova, Artemisia tridentata ssp. vaseyana, Cercocarpus intricatus, Cercocarpus montanus, Ericameria nauseosa, Fallugia paradoxa, Purshia stansburiana, Quercus gambelii, Quercus x pauciloba, Ribes cereum, Ribes inerme, Robinia neomexicana, and Symphoricarpos oreophilus. The most common herbaceous dominants may include Achnatherum hymenoides, Andropogon hallii, Bromus inermis, Carex inops ssp. heliophila, Carex rossii, Carex siccata, Festuca thurberi, Leucopoa kingii, Leymus salinus, Poa fendleriana, and Pteridium aquilinum. Within the Rocky Mountains, these forests and woodlands grow at elevations between 1800-2600 m (6000-8500 feet). In the Black Hills and northeastern Wyoming, it can be found from 1080-2100 m (3600-7000 feet). Sites are dry/dry-mesic to xeric, and soils are generally well-drained and coarse-textured. Occurrences can be found on slopes of a variety of aspects and pitches, but is most often on gentle to moderate, northeast- to northwest-facing slopes.
Diagnostic Characteristics: Pinus ponderosa (primarily var. scopulorum and var. brachyptera) is the predominant conifer; Pseudotsuga menziesii, Pinus edulis, Pinus contorta, Populus tremuloides, and Juniperus spp. may also be present in the tree canopy. Understories are characterized by dense shrubs, graminoids or sparse, barren ground.
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: These are forest stands of needle-leaved evergreen trees 10-30 m in height. Associated trees are typically needle-leaved evergreen species, but cold-deciduous and broad-leaved evergreen trees may form a subcanopy. The understory is typically dominated by cespitose graminoids, sclerophyllous or cold-deciduous shrubs.
Floristics: This alliance includes forests and woodlands dominated by Pinus ponderosa. Structurally, these are open to closed with tree canopy cover ranging from 20-100%. The understory may include dense stands of shrubs or be dominated by grasses, sedges, or other herbaceous species. Stands usually have younger cohorts of Pinus ponderosa present and may be less open than in the past. Associated trees vary widely across the range of this alliance and may include Abies concolor, Juniperus scopulorum, Pinus contorta, Pinus edulis, Pinus flexilis, Pinus strobiformis, Populus tremuloides, and Pseudotsuga menziesii. A shrub layer may be prominent or nearly absent, depending on location and disturbance history. Common dominant shrubs may include Arctostaphylos patula, Arctostaphylos pungens, Arctostaphylos uva-ursi, Artemisia nova, Artemisia tridentata ssp. vaseyana, Cercocarpus intricatus, Cercocarpus montanus, Ericameria nauseosa, Fallugia paradoxa, Purshia stansburiana, Quercus gambelii, Quercus x pauciloba, Ribes cereum, Ribes inerme, Robinia neomexicana, and Symphoricarpos oreophilus. The herbaceous layer tends to vary inversely with shrub cover, but is composed primarily of graminoids. The most common herbaceous dominants may include Achnatherum hymenoides, Andropogon hallii, Bromus inermis, Carex inops ssp. heliophila, Carex rossii, Carex siccata, Festuca thurberi, Leucopoa kingii, Leymus salinus, Poa fendleriana, and Pteridium aquilinum.
Dynamics: Pinus ponderosa is a drought-resistant, shade-intolerant conifer which usually occurs at lower treeline in the major ranges of the western United States. Historically, surface fires and drought were influential in maintaining open canopy conditions. With settlement and subsequent fire suppression, stands have become denser than they once were. Presettlement fire regimes were primarily frequent (5- to 15-year return intervals) including low-intensity surface fires triggered by lightning strikes or deliberately set by Native Americans. With fire suppression and increased fuel loads, fires are now less frequent and often become intense crown fires which can kill mature Pinus ponderosa. Presently, many stands contain understories of more shade-tolerant species, such as Pseudotsuga menziesii and/or Abies spp., which may be affecting fuel loads and may alter future fire regimes. Establishment is erratic and believed to be linked to periods of adequate soil moisture, good seed crops, and the availability of bare, unshaded mineral substrate. At drier sites, competition from adjacent grassland or shrubland vegetation can strongly affect seedling survival (Burns and Honkala 1990a).
Environmental Description: These forests and woodlands typically occur at the lowest elevations of the coniferous forest and woodland zone within their range. These are among the driest forested habitats in the western United States, but quantity and timing of precipitation vary greatly across the range of this vegetation. Generally, these woodlands occur in areas which receive 25-60 cm of precipitation annually, with at least some seasonal drought. Fire is a key factor in maintaining the relatively open canopies characteristic of these stands, but soil drought or infertility may be equally important in some areas. Within the Rocky Mountains, Pinus ponderosa grows at elevations between 1800 and 2600 m (6000-8500 feet) (Mehl 1992). In the Black Hills and northeastern Wyoming, it can be found from 1080-2100 m (3600-7000 feet). Soils are highly variable across the range of this type, and are derived from igneous, metamorphic, and sedimentary materials. The most characteristic soil features are good aeration and drainage, circumneutral to slightly acidic pH, an abundance of mineral material, and periods of drought during the growing season. It can be found on slopes of a variety of aspects and pitches, but is most often on gentle to moderate, northeast- to northwest-facing slopes. Some stands may occur as edaphic climax communities on very skeletal, infertile, and/or excessively drained soils, such as cinder or lava fields.
Geographic Range: This alliance is found from northwestern Wyoming, the Black Hills of South Dakota, south through the Rocky Mountains of Colorado and into New Mexico, and a few scattered stands in western Texas. In Arizona, it occurs on the Mogollon Rim north into the Colorado Plateau region and west into scattered locations of the Great Basin.
Nations: MX,US
States/Provinces: AZ, CA?, CO, ID?, MT, MXCHH, MXSON, ND, NE, NM, NV, SD, TX, UT, WY
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.899522
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: GNR
Greasons: No Data Available
Concept Lineage: A.124, A.530, in parts
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: >< Pinus ponderosa (Ponderosa pine forest) Alliance (Sawyer et al. 2009) [87.010.00]
? Pinus ponderosa Alliance (Ponderosa pine forest) (Buck-Diaz et al. 2012)
>< IA1b. Ponderosa Pine Forest (Allard 1990)
>< Interior Ponderosa Pine - Black Hills (Mehl 1992)
>< Interior Ponderosa Pine - Front Range (Mehl 1992)
>< Interior Ponderosa Pine: 237 (Eyre 1980)
>< Ponderosa Pine Series (Sawyer and Keeler-Wolf 1995)
? Pinus ponderosa Alliance (Ponderosa pine forest) (Buck-Diaz et al. 2012)
>< IA1b. Ponderosa Pine Forest (Allard 1990)
>< Interior Ponderosa Pine - Black Hills (Mehl 1992)
>< Interior Ponderosa Pine - Front Range (Mehl 1992)
>< Interior Ponderosa Pine: 237 (Eyre 1980)
>< Ponderosa Pine Series (Sawyer and Keeler-Wolf 1995)
- Allard, D. J. 1990. Southeastern United States ecological community classification. Interim report, Version 1.2. The Nature Conservancy, Southeast Regional Office, Chapel Hill, NC. 96 pp.
- Buck-Diaz, J., S. Batiuk, and J. M. Evens. 2012. Vegetation alliances and associations of the Great Valley ecoregion, California. California Native Society, Sacramento, CA. [http://cnps.org/cnps/vegetation/pdf/great_valley_eco-vegclass2012.pdf]
- Burns, R. M., and B. H. Honkala, technical coordinators. 1990a. Silvics of North America: Volume 1. Conifers. Agriculture Handbook 654. USDA Forest Service, Washington, DC. 675 pp.
- Diamond, D. D. 1993. Classification of the plant communities of Texas (series level). Unpublished document. Texas Natural Heritage Program, Austin. 25 pp.
- Eyre, F. H., editor. 1980. Forest cover types of the United States and Canada. Society of American Foresters, Washington, DC. 148 pp.
- Faber-Langendoen, D., J. Drake, M. Hall, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, M. Russo, K. Schulz, L. Sneddon, K. Snow, and J. Teague. 2013-2019b. Screening alliances for induction into the U.S. National Vegetation Classification: Part 1 - Alliance concept review. NatureServe, Arlington, VA.
- Mehl, M. S. 1992. Old-growth descriptions for the major forest cover types in the Rocky Mountain Region. Pages 106-120 in: M. R. Kaufmann, W. H. Moir, and R. L. Bassett. Old-growth forests in the southwest and Rocky Mountain regions. Proceedings of the old-growth forests in the Rocky Mountains and Southwest conference, Portal, AZ. March 9-13, 1992. General Technical Report RM-213. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO.
- Sawyer, J. O., T. Keeler-Wolf, and J. Evens. 2009. A manual of California vegetation. Second edition. California Native Plant Society, Sacramento CA. 1300 pp.
- Sawyer, J. O., and T. Keeler-Wolf. 1995. A manual of California vegetation. California Native Plant Society, Sacramento. 471 pp.