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	CEGL005971 Populus deltoides (ssp. wislizeni, ssp. monilifera) / Forestiera pubescens Flooded Forest
					Type Concept Sentence: No Data Available
				
			
								Common (Translated Scientific) Name: (Rio Grande Cottonwood, Plains Cottonwood) / Stretchberry Flooded Forest
							
							
								Colloquial Name: No Data Available
							
							
								Hierarchy Level:  Association
							
							
								Type Concept: This mature riparian forest association is found in the San Juan and Rio Grande watersheds in northern and central New Mexico, the Animas River watershed in southwestern Colorado, and is likely present in the Pecos drainage farther to the east. It occurs along low-gradient rivers of wide lowland valleys at elevations from 1530 to 1800 m (5000-5900 feet). Sites range from relatively dry, elevated terraces that are rarely flooded, to more frequently flooded mid-elevation sidebars and island bars of low-gradient rivers. Soils are moist or dry, poorly developed Entisols or, where some soil development has occurred on older terraces, Inceptisols. Soil textures are coarse-loamy throughout the profile, or with sandy layers overlain by finer loam or silt. All soils have high plant-available water (8.5% on average), and the water table is usually within 2 m of the surface during the growing season. This community type is characterized by mature, often dense and closed canopies of Populus deltoides ssp. wislizeni or Populus deltoides ssp. monilifera with occasional Salix gooddingii in the subcanopy. Other trees may be present in the subcanopy but are not normally abundant. Populus deltoides saplings are rare or absent. The shrubs are well-represented to abundant (10-75% cover) and dominated by Forestiera pubescens var. pubescens with Rhus trilobata and Amorpha fruticosa common. In Colorado, Elaeagnus angustifolia and Tamarix ramosissima can also be present. The twining, woody vines of Parthenocissus quinquefolia and Clematis ligusticifolia can often be found among downed logs or wrapped around trees and shrubs. The herbaceous layer is sparse to well-represented (10-15% cover) and is a mix of grasses and forbs that reflect the relatively drier habitat. Overall, species diversity is high with 81 species recorded for the type (although 24-30% were exotics). As a keystone species, the reproduction of Populus deltoides after flooding (and sufficient subsequent base flows) is critical to the sustainability of this community.
							
							
								Diagnostic Characteristics: No Data Available
							
							
								Rationale for Nominal Species or Physiognomic Features: No Data Available
							
							
								Classification Comments: The community is naturally distributed along the floodplains of larger streams and rivers but may be declining due to encroachment by exotic species and altered hydrologic regimes. Where it occurs along stream reaches that have been significantly altered in some way (i.e., jetty jacks, dams, and irrigation diversion), there is a wide range of soil and hydrological conditions in which this community occurs. Occasionally, floodplains may become highly altered, leaving the community far from the active channel, thus reducing flooding and stopping reproduction. With increasing disturbance from fire, the community becomes highly susceptible to further invasion by exotics, particularly by Elaeagnus angustifolia, Tamarix ramosissima, and Ulmus pumila. Elaeagnus angustifolia is common in most stands (particularly more mesic ones) and is the most probable successional exotic species. Effective restoration of these stands to enhance biodiversity, quality, and condition requires emulating a natural hydrological regime.
							
							
								Similar NVC Types: No Data Available
							
							
								note: No Data Available
							
							
						
								Physiognomy and Structure: No Data Available
							
							
								Floristics: This community type is characterized by mature, often dense and closed canopies of Populus deltoides ssp. wislizeni or Populus deltoides ssp. monilifera with a shrubby subcanopy of Forestiera pubescens var. pubescens. In the mature stand, cottonwood seedlings or saplings are rare or nonexistent. Other trees, such as Juniperus monosperma, Salix gooddingii, and the exotics Elaeagnus angustifolia, Ulmus pumila, or Morus alba, may be present in the subcanopy but are not normally abundant. The shrub layer may also include scattered Rhus trilobata and Ericameria nauseosa (= Chrysothamnus nauseosus). The twining, woody vines of Parthenocissus quinquefolia and Clematis ligusticifolia can often be found among downed logs or wrapped around trees and shrubs. The herbaceous layer is sparse to well-represented (10-15% cover) and is a mix of grasses and forbs such as Sporobolus airoides, Achnatherum hymenoides (= Oryzopsis hymenoides), and Solidago canadensis that reflect the relatively drier habitat. Overall, species diversity is high (81 species recorded for the type), with 24 (30%) of those being exotics. The majority of the diversity is found in the herbaceous layer (51 species), including 9 native wetland indicator species; they are Distichlis spicata, Juncus arcticus ssp. littoralis (= Juncus balticus), Muhlenbergia asperifolia, Schoenoplectus pungens (= Scirpus pungens), Anemopsis californica, Asclepias incarnata, Equisetum laevigatum, Euthamia occidentalis, and Sagittaria cuneata.
							
							
								Dynamics:  No Data Available
							
						
								Environmental Description:  This type occurs in lowland river valleys at elevations that range from 1530 to 1800 m (5000-5900 feet). Sites range from relatively dry, elevated terraces that are rarely flooded, to more frequently flooded mid-elevation sidebars and island bars of low-gradient rivers. Soils are moist or dry poorly developed Entisols or, where some soil development has occurred on older terraces, Inceptisols. Soil textures are coarse-loamy throughout the profile, or with sandy layers overlain by finer loam or silt. All soils have high plant-available water (8.5% on average), and the water table is usually within 2 m of the surface during the growing season.
							
						
								Geographic Range: This association is found in the San Juan and Rio Grande watersheds in northern and central New Mexico, southwestern Colorado, and may occur farther west into Utah and Arizona.
							
							
								Nations: US
							
							
								States/Provinces:  AZ?, CO, NM, UT?
							
							
								Plot Analysis Summary:  
								http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.737595
							
						
								Confidence Level: Low
							
							
								Confidence Level Comments: No Data Available
							
						
								Grank: G2
							
							
								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.Nd Western North American Interior Flooded Forest Division | D013 | 1.B.3.Nd | 
| Macrogroup | 1.B.3.Nd.2 Interior Warm & Cool Desert Riparian Forest Macrogroup | M036 | 1.B.3.Nd.2 | 
| Group | 1.B.3.Nd.2.b Western Interior Riparian Forest & Woodland Group | G797 | 1.B.3.Nd.2.b | 
| Alliance | A3802 Rio Grande Cottonwood - Plains Cottonwood Riparian Forest Alliance | A3802 | 1.B.3.Nd.2.b | 
| Association | CEGL005971 (Rio Grande Cottonwood, Plains Cottonwood) / Stretchberry Flooded Forest | CEGL005971 | 1.B.3.Nd.2.b | 
								Concept Lineage: No Data Available
							
							
								Predecessors: No Data Available
							
							
								Obsolete Names: No Data Available
							
							
								Obsolete Parents: No Data Available
							
						
								Synonomy: = Populus deltoides / Forestiera pubescens Woodland (Carsey et al. 2003a)
= Populus deltoides ssp. wislizeni / Forestiera pubescens Woodland Association (Donnelly et al. 2006)
= Plains Cottonwood/New Mexico Olive CT (Muldavin et al. 2000a)
						= Populus deltoides ssp. wislizeni / Forestiera pubescens Woodland Association (Donnelly et al. 2006)
= Plains Cottonwood/New Mexico Olive CT (Muldavin et al. 2000a)
- 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.
 - Donnelly, P., D. Lindsey, E. Muldavin, Y. Chauvin, and A. Browder. 2006. Vegetation communities of Bosque del Apache National Wildlife Refuge. Prepared by U.S. Fish and Wildlife Service, National Wildlife Refuge Remote Sensing Lab, Albuquerque, NM, and Natural Heritage New Mexico, University of New Mexico, Albuquerque. Final report submitted to U.S. Fish and Wildlife Service, Southwest Region (R2), National Wildlife Refuge System (NWR), NWR Remote Sensing Lab, Division of Planning. 27 pp. [http://www.fws.gov/data/documents/BDA%20NVCS%20Veg%20Community%20Report%20Example.pdf]
 - 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.
 - NHNM [Natural Heritage New Mexico]. No date. Unpublished data on file. Natural Heritage New Mexico, University of New Mexico, Albuquerque.
 - Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.