Print Report

A0842 Tamarix spp. Ruderal Riparian Scrub Alliance

Type Concept Sentence: This alliance is composed of shrublands dominated by introduced species of Tamarix, including Tamarix chinensis, Tamarix gallica, Tamarix parviflora, and Tamarix ramosissima. It forms moderately dense to dense thickets on banks of larger streams, rivers and playas across the southwestern U.S. and northern Mexico.


Common (Translated Scientific) Name: Tamarisk species Ruderal Riparian Scrub Alliance

Colloquial Name: Ruderal Tamarisk Riparian Scrub

Hierarchy Level:  Alliance

Type Concept: This alliance is composed of shrublands dominated by introduced species of Tamarix, including Tamarix chinensis, Tamarix gallica, Tamarix parviflora, and Tamarix ramosissima. It forms moderately dense to dense thickets on banks of larger streams, rivers and playas across the southwestern U.S. and northern Mexico. Introduced from the Mediterranean, Tamarix spp. have become naturalized in various sites, including salt flats, springs, and especially along streams and regulated rivers, often replacing Salix or Prosopis spp. shrublands or other native vegetation. A remnant herbaceous layer may be present, depending on the age and density of the shrub layer. These species have become a critical nuisance along most large rivers in the semi-arid western U.S.

Diagnostic Characteristics: Riparian woodlands and washes dominated by Tamarix spp.

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: Stands also occur in Oklahoma, and this alliance includes them as well.

Similar NVC Types: No Data Available
note: No Data Available

Physiognomy and Structure: No Data Available

Floristics: This alliance consists of shrublands with moderate to dense cover of a tall-shrub layer that is solely or strongly dominated by Tamarix, including (commonly) Tamarix chinensis, Tamarix gallica, Tamarix parviflora, and Tamarix ramosissima. Other introduced species of Tamarix have been documented in the U.S., but whether these form full stands is yet to be documented. Additional Tamarix species include Tamarix africana, Tamarix aphylla, Tamarix aralensis, Tamarix canariensis, and Tamarix tetragyna (Kartesz 1999). Other native shrubs may be present and include species of Salix (especially Salix exigua) and Prosopis, Rhus trilobata, and Sarcobatus vermiculatus, but with low cover (if shrub species are codominant, then stand may be classified as a native shrubland type). Scattered native Acer negundo, Elaeagnus angustifolia, Populus spp., or Salix amygdaloides trees may also be present. Depending on stand age and density of the shrub layer, an herbaceous layer may be present. Associated native species include Distichlis spicata, Sporobolus airoides, and introduced forage species such as Agrostis gigantea, Agrostis stolonifera, and Poa pratensis. Other introduced herbaceous species such as Conyza canadensis, Lepidium latifolium, and Polypogon monspeliensis may also be present.

Dynamics:  Tamarix spp. are extremely drought- and salt-tolerant, produce prolific wind-dispersed seeds over much of the growing season, can resprout after burning or cutting, and, if kept moist, buried or broken branches will develop adventitious roots and grow. Stands seem to favor disturbed and flow-regulated rivers, but establish well in pristine areas, too. Once established, stands are extremely difficult to eradicate, requiring cutting and herbicide application on stumps to prevent resprouting (Smith and Douglas 1989).

In California, tamarisk species are among the most invasive, widely distributed, and troublesome non-natives to infest wetlands. Multiple, interacting factors facilitate tamarisk invasion, including intentional planting for erosion control and windbreaks; land conversion to agriculture; reduced flood frequencies after damming rivers; changing and stabilizing waterflows, times, and rates downstream from reservoirs; and increased salinity levels in the rivers from evaporation in the reservoirs (Everitt 1980). Tamarisk vigorously sprouts and increases flowering and seed production after fire. Mixed riparian stands often change to tamarisk-dominated stands after fires (Zouhar 2003b, Brooks and Minnich 2006). Active programs to remove tamarisk are ongoing in the state (Lovich 2000). Discouraging tamarisk establishment by biological and mechanical control is the most effective method of control. Once established in large stands, control and eradication efforts are difficult and costly; many managers recommend integrated management approaches (Lovich 2000, Zouhar 2003b, Carpenter 2005).

Environmental Description:  These widespread shrublands are common along larger streams, rivers, and around playas. Elevation ranges from 75 m below sea level to 1860 m. Sites include riverbanks, floodplains, basins, sandbars, side channels, springs, salt flats, and other saline habitats. Substrates are commonly thin sandy loam soil over alluvial deposits of sand, gravel or cobbles. Stands grow especially well along regulated rivers and rivers with agricultural runoff that increase the salts in the water.

Geographic Range: This alliance is found throughout the southwestern U.S. and northern Mexico.

Nations: MX,US

States/Provinces:  AZ, CA, CO, MT, MXCHH, MXCOA, MXSON, NM, NV, OK, TX, UT, WY




Confidence Level: Low - Poorly Documented

Confidence Level Comments: No Data Available

Grank: GNA

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: = Tamarix spp. (Tamarisk thickets) Semi-natural Stands (Sawyer et al. 2009) [63.810.00]
? Tamarix chinensis Community Type (Hansen et al. 1995)
? Tamarix chinensis shrubland alliance (Hoagland 1998a)
? Tamarix pentandra Community Type (Szaro 1989)
? Tamarix ramosissima (Salt cedar) Association (Nachlinger and Reese 1996)
= Tamarix spp. Semi-Natural Shrubland Stands (Evens et al. 2012)
= Tamarix spp. Semi-Natural Stands (Tamarisk thickets) (Buck-Diaz et al. 2012)
= Tamarix spp. Semi-natural Shrubland Alliance (Evens et al. 2014)
= Tamarix spp. Shrubland Semi-Natural Alliance (CNPS 2017) [63.810.00]
? Salt cedar series (Paysen et al. 1980)
= Saltcedar Alliance (Muldavin et al. 2000a)
? Saltcedar Series (Dick-Peddie 1993)
= Tamarisk Scrub (#63810) (Holland 1986b)
= Tamarisk series (Sawyer and Keeler-Wolf 1995)

Concept Author(s): M.S. Reid and K.A. Schulz, in Faber-Langendoen et al. (2013)

Author of Description: G. Kittel

Acknowledgements: No Data Available

Version Date: 12-18-14

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