Print Report
CEGL000654 Populus angustifolia / Salix exigua Riparian Woodland
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Narrowleaf Cottonwood / Narrowleaf Willow Riparian Woodland
Colloquial Name: No Data Available
Hierarchy Level: Association
Type Concept: The type is widespread in mountainous regions of the San Juan, Pecos, and Rio Grande river basins in northern and central New Mexico and widely distributed throughout the Rocky Mountain region and Intermountain West. It is found in wide to narrow valleys at mid to upper elevations from 1670 to 2360 m (5480-7750 feet). It occurs on streamside alluvial bars that border perennial rivers and intermittent streams of low to moderate gradients (0.7-2.8%). In Colorado, this riparian woodland occupies point bars, gravel bars, benches and low areas that are flooded annually. It is a very common plant community of young seedling and sapling Populus angustifolia intermixed with Salix exigua. Sites are typically flooded every five years, sometime more often, and most are within the 25-year floodplain. Stream channel materials are usually coarse and composed of cobbles or gravel. Soils are young and weakly developed Entisols with wet (aquic) conditions within the top 50 cm or at least within rooting depth. They are well-drained sands and sandy loams mixed with gravels and cobbles. This type is characterized by middle-aged stands of Populus angustifolia in an open upper canopy, with a shrubby understory dominated by Salix exigua. Populus angustifolia saplings (derived from root sprouts) are common beneath the canopy. Other shrubs such as Salix irrorata may be well-represented but clearly subordinate to Salix exigua. The herbaceous layer is very diverse, with 98 species recorded for the type, 23 of which are native wetland indicators.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: Several other Salix species may be present, and the canopy may have other species of Populus as well.
The community is widely distributed on younger depositional bars of moderate-sized streams with unregulated flows and few diversions. Since the stands are well-adapted to flooding, they are well-suited for streambank stabilization. Typically found in wider valleys where ranches and livestock are common, the coarse-textured soils are not susceptible to compaction. However, the streamside location of these stands makes them prone to heavy usage by livestock. Without careful management, woody components such as saplings and shrubs decrease. Under continuous pressure from grazing, these stands have limited self-sustainability and are eventually replaced by non-cottonwood-dominated stands prone to streambank erosion. Managers should maintain a buffer strip of cottonwoods along streambanks to avoid erosion. When grazing pressure is lessened, regrowth of cottonwoods is rapid, riparian shrubs return, and streambanks become more stable. In addition, species diversity and wildlife habitat increase. Populus angustifolia and Salix exigua are obligate riparian species which require flooding for reproduction, growth, and maintenance. Depending on the depth of the water table, these stands will respond positively to fire disturbance with rapid regrowth. Both species are highly palatable to beaver and livestock, and potential usage is high.
Medina (1986) described a Populus acuminata / Salix exigua community type in southwestern New Mexico that is very similar to this one. This type has been well-documented in Colorado (Ramaley 1942, Woodbury et al. 1961, Hess 1981, Baker 1984a, Hess and Alexander 1986, Johnston 1987, Kittel and Lederer 1993, Kittel et al. 1994, 1996) and in Nevada (Manning and Padgett 1995).
The community is widely distributed on younger depositional bars of moderate-sized streams with unregulated flows and few diversions. Since the stands are well-adapted to flooding, they are well-suited for streambank stabilization. Typically found in wider valleys where ranches and livestock are common, the coarse-textured soils are not susceptible to compaction. However, the streamside location of these stands makes them prone to heavy usage by livestock. Without careful management, woody components such as saplings and shrubs decrease. Under continuous pressure from grazing, these stands have limited self-sustainability and are eventually replaced by non-cottonwood-dominated stands prone to streambank erosion. Managers should maintain a buffer strip of cottonwoods along streambanks to avoid erosion. When grazing pressure is lessened, regrowth of cottonwoods is rapid, riparian shrubs return, and streambanks become more stable. In addition, species diversity and wildlife habitat increase. Populus angustifolia and Salix exigua are obligate riparian species which require flooding for reproduction, growth, and maintenance. Depending on the depth of the water table, these stands will respond positively to fire disturbance with rapid regrowth. Both species are highly palatable to beaver and livestock, and potential usage is high.
Medina (1986) described a Populus acuminata / Salix exigua community type in southwestern New Mexico that is very similar to this one. This type has been well-documented in Colorado (Ramaley 1942, Woodbury et al. 1961, Hess 1981, Baker 1984a, Hess and Alexander 1986, Johnston 1987, Kittel and Lederer 1993, Kittel et al. 1994, 1996) and in Nevada (Manning and Padgett 1995).
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: This type is characterized by middle-aged stands of Populus angustifolia in an open upper canopy, with a shrubby understory dominated by Salix exigua. Populus angustifolia saplings (derived from root sprouts) are common beneath the canopy. The canopy may contain individuals of Populus deltoides ssp. deltoides or Acer negundo. Other shrubs, such as Salix irrorata or Salix monticola, may be well-represented but clearly subordinate to Salix exigua. Depending on hydrologic conditions and canopy closure, the herbaceous layer may be sparse to dense and is generally highly diverse, with 98 species recorded for the type, 23 of which are native wetland indicators. The most common and abundant native wetland species are Eleocharis palustris, Juncus arcticus ssp. littoralis (= Juncus balticus), Juncus saximontanus, Equisetum arvense, Equisetum laevigatum, Epilobium ciliatum, Prunella vulgaris, Schoenoplectus pungens (= Scirpus pungens), and Schoenoplectus tabernaemontani (= Scirpus tabernaemontani). The most consistent grass is the introduced Agrostis stolonifera or Agrostis gigantea. Other forb species can also be prevalent, including Melilotus officinalis, Glycyrrhiza lepidota, and Xanthium strumarium.
Dynamics: No Data Available
Environmental Description: The type is found in wide valleys to narrow canyons at mid to upper elevations from 1670 to 2360 m (5480-7750 feet). It occurs on streamside alluvial bars that border perennial rivers and intermittent streams of low to moderate gradients (0.7-2.8%). In the Colorado Plateau, some stands occupy canyon alcoves. Sites are typically flooded every five years, sometime more often, and most are within the 25-year floodplain. Stream channel materials are usually coarse and composed of cobbles or gravel. Soils are young and weakly developed Entisols with wet (aquic) conditions within the top 50 cm or at least within rooting depth. They are well-drained sands and sandy loams mixed with gravels and cobbles.
Geographic Range: This association is widespread in mountainous regions of the San Juan, Pecos, and Rio Grande river basins in northern and central New Mexico and widely distributed throughout the Rocky Mountain region and Intermountain West.
Nations: US
States/Provinces: CO, NM, NV, UT
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.689856
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G4
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 | A3759 Narrowleaf Cottonwood Riparian Forest Alliance | A3759 | 1.B.3.Nc.1.a |
Association | CEGL000654 Narrowleaf Cottonwood / Narrowleaf Willow Riparian Woodland | CEGL000654 | 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: ? Populus acuminata / Salix exigua Community Type (Medina 1986)
= Populus angustifolia / Salix exigua Plant Association (Durkin et al. 1994b)
= Populus angustifolia / Salix exigua Plant Association (Durkin et al. 1995a)
= Populus angustifolia / Salix exigua Woodland (Carsey et al. 2003a)
= Populus angustifolia/Salix exigua (Kittel et al. 1999b)
= Narrowleaf Cottonwood/Coyote Willow CT (Muldavin et al. 2000a)
= Narrowleaf cottonwood/coyote willow (Populus angustifolia/Salix exigua) Plant Association (Kittel et al. 1999a)
= Narrowleaf cottonwood/coyote willow (Populus angustifolia/Salix exigua) Plant Association (Kittel et al. 1997a)
= Populus angustifolia / Salix exigua Plant Association (Durkin et al. 1994b)
= Populus angustifolia / Salix exigua Plant Association (Durkin et al. 1995a)
= Populus angustifolia / Salix exigua Woodland (Carsey et al. 2003a)
= Populus angustifolia/Salix exigua (Kittel et al. 1999b)
= Narrowleaf Cottonwood/Coyote Willow CT (Muldavin et al. 2000a)
= Narrowleaf cottonwood/coyote willow (Populus angustifolia/Salix exigua) Plant Association (Kittel et al. 1999a)
= Narrowleaf cottonwood/coyote willow (Populus angustifolia/Salix exigua) Plant Association (Kittel et al. 1997a)
- Baker, W. L. 1984a. A preliminary classification of the natural vegetation of Colorado. Great Basin Naturalist 44(4):647-676.
- Beidleman, R. G. 1954. The cottonwood river-bottom community as a vertebrate habitat. Unpublished dissertation, University of Colorado, Boulder. 358 pp.
- 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/]
- 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.
- Coles, J., A. Tendick, J. Von Loh, G. Bradshaw, G. Manis, A. Wight, G. Wakefield, and A. Evenden. 2010. Vegetation classification and mapping project report, Black Canyon of the Gunnison National Park. Natural Resource Technical Report NPS/NCPN/NRTR--2010/361. National Park Service, Fort Collins, CO.
- Coles, J., D. Cogan, D. Salas, A. Wight, G. Wakefield, J. Von Loh, and A. Evenden. 2008a. Vegetation classification and mapping project report, Dinosaur National Monument. Natural Resource Technical Report NPS/NCPN/NRTR-2008/112. National Park Service, Fort Collins, CO. 814 pp.
- DeLeuw, Cather & Company. 1977. Vegetation sampling (Glenwood Canyon). Unpublished report prepared by DeLeuw, Cather & Company, Consulting Engineers and Planners, Chicago, Illinois for Colorado Division of Highways, Glenwood Springs, CO.
- Durkin, P., M. Bradley, E. Muldavin, and P. Mehlhop. 1994b. A riparian/wetland vegetation community classification of New Mexico: Pecos River Basin. Unpublished report for New Mexico Environment Department Surface Water Quality Bureau.
- Durkin, P., M. Bradley, E. Muldavin, and P. Mehlhop. 1995a. Riparian/wetland vegetation community classification of Rio Grande: A classification and site evaluation. Unpublished report for New Mexico Environment Department Surface Water Quality Bureau. New Mexico Natural Heritage Program, Albuquerque.
- Hess, K. 1981. Phyto-edaphic study of habitat types of the Arapaho-Roosevelt National Forest, Colorado. Unpublished dissertation, Colorado State University, Fort Collins. 558 pp.
- Hess, K., and R. R. Alexander. 1986. Forest vegetation of the Arapaho and Roosevelt national forests in northcentral Colorado: A habitat type classification. Research Paper RM-266. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO. 48 pp.
- 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.
- Keammerer, W. R. 1974a. Vegetation of the Grand Valley area. Pages 73-117 in: Ecological inventory of the Grand Valley area Unpublished report prepared for the Colony Development Operation, Atlantic Richfield Company, Denver, CO.
- Kittel, G. M., and N. D. Lederer. 1993. A preliminary classification of the riparian vegetation of the Yampa and San Miguel/Dolores river basins. Unpublished report prepared for Colorado Department of Health and the Environmental Protection Agency by The Nature Conservancy, Colorado Field Office, Boulder.
- 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. 1997a. A classification of the riparian vegetation of the South Platte Basin (and part of Republican River Basin), Colorado. Submitted to Colorado Department of Natural Resources and the Environmental Protection Agency, Region VIII. Prepared by Colorado Natural Heritage Program, Colorado State University, Fort Collins.
- 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 A. McMullen. 1996. A classification of the riparian vegetation of the Lower South Platte and parts of the Upper Arkansas River basins, Colorado. Submitted to Colorado Department of Natural Resources and the Environmental Protection Agency, Region VIII. Prepared by Colorado Natural Heritage Program, Fort Collins. 243 pp.
- Manning, M. E., and W. G. Padgett. 1995. Riparian community type classification for Humboldt and Toiyabe national forests, Nevada and eastern California. USDA Forest Service, Intermountain Region. 306 pp.
- Medina, A. L. 1986. Riparian plant communities of the Fort Bayard watershed in southwestern New Mexico. Southwestern Naturalist 31(3):345-359.
- Muldavin, E., J. Stevens, Y. Chauvin, A. Browder, T. Neville, K. Sever, and T. Talbot. 2012g. Vegetation survey and accuracy assessment of vegetation mapping at Fort Union National Monument, New Mexico. Natural Resource Report NPS/FOUN/NRR--2012/553. National Park Service, Fort Collins, CO. 102 pp. [http://www.usgs.gov/core_science_systems/csas/vip/parks/foun.html]
- Muldavin, E., P. Durkin, M. Bradley, M. Stuever, and P. Mehlhop. 2000a. Handbook of wetland vegetation communities of New Mexico. Volume I: Classification and community descriptions. Final report to the New Mexico Environment Department and the Environmental Protection Agency prepared by the New Mexico Natural Heritage Program, University of New Mexico, Albuquerque.
- Muldavin, E., Y. Chauvin, P. Neville, T. Neville, L. Arnold, P. Arbetan, and A. Fettes. 2012b. A vegetation classification and map: Pecos National Historical Park. Natural Resource Technical Report NPS/SOPN/NRTR--2012/601. National Park Service, Fort Collins, CO.
- Ramaley, F. 1942. Vegetation of the San Luis Valley in southern Colorado. University of Colorado Studies, Series D, 1:231-277.
- 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. E., J. Stevens, K. Schulz, M. Artmann, B. Friesen, S. Blauer, E. W. Schweiger, and A. Valdez. 2010b. Vegetation classification and mapping project report: Great Sand Dunes National Park and Preserve. Natural Resource Report NPS/ROMN/NRR--2010/179. National Park Service, Fort Collins, CO.
- Tendick, A., J. Coles, P. Williams, G. Bradshaw, G. Manis, A. Wight, G. Wakefield, and A. Evenden. 2010. Vegetation classification and mapping project report, Curecanti National Recreation Area. Natural Resource Technical Report NPS/NCPN/NRTR--2010/408. National Park Service, Fort Collins, CO. 797 pp.
- Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.
- Woodbury, A. M., S. D. Durrant, and S. Flowers. 1961. A survey of vegetation in the Navajo Reservoir basin. University of Utah Anthropological Papers 51, Salt Lake City. 99 pp.