Natural Resources
Conservation Service
Ecological site R047XA016UT
Loamy Bottom
(basin wildrye)
Last updated: 2/05/2025
Accessed: 07/11/2026
-
Search
Major Land Resource Area or ecological site by name and/or ID.
PreviousSectionsNextGeneral information
Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.
MLRA notes
Major Land Resource Area (MLRA): 047X–Wasatch and Uinta Mountains
MLRA 47 occurs in Utah (86 percent), Wyoming (8 percent), Colorado (4 percent), and Idaho (2 percent). It encompasses approximately 23,825 square miles (61,740 square kilometers). The northern half of this area is in the Middle Rocky Mountains Province of the Rocky Mountain System. Parts of the western edge of this MLRA are in the Great Basin Section of the Basin and Range Province of the Intermontane Plateaus. The MLRA includes the Wasatch Mountains, which trend north and south. The steeply sloping, precipitous Wasatch Mountains have narrow crests and deep valleys. Active faulting and erosion are a dominant force in controlling the geomorphology of the area.
The mountains in this area are primarily fault blocks that have been tilted up. Alluvial fans at the base of the mountains are recharge zones for the basin fill aquifers. An ancient shoreline of historic Bonneville Lake is evident on the footslopes along the western edge of the area. Rocks exposed in the mountains are mostly Mesozoic and Paleozoic sediments.
The average precipitation is from 12 to 16 inches in the valleys and can range up to 73 inches in the mountains. Peak precipitation occurs in the winter months. The average annual temperature is 30 to 50 degrees Fahrenheit (-1 to 15 C). The freeze-free period averages 140 days and ranges from 60 to 220 days, generally decreasing in length with elevation.
The dominant soil orders in this MLRA are Entisols, Inceptisols, and Mollisols. The lower elevations are dominated by a frigid temperature regime, while the higher elevations experience cryic temperature regimes. The soil moisture regime is typically xeric. The minerology is generally mixed and the soils are very shallow to very deep, generally well drained, and loamy or loamy-skeletal.LRU notes
This LRU includes the Wasatch Mountains which tend to run north and south. These steeply sloping, precipitous mountains have narrow crests and deep valleys. They are primarily fault blocks that have been tilted up. The alluvial fans located at the base of these mountains are important recharge zones for valley aquifers.
Ecological site concept
The soils of this site formed mostly in alluvium from andesite, dacite, basalt, or tuff.. Surface soils are very dark grayinsh brown and fine sandy loam in texture. Rock fragments may be present on the soil surface and throughout the profile, but make up less than 35 percent of the soil volume. These soils are deep to very deep, moderately well-drained, and have moderately permeability. pH is neutral.. Available water-holding capacity ranges from 3 to 5.2 inches of water in the upper 60 inches of soil. The soil moisture regime is mostly xeric and the soil temperature regime is frigid. Precipitation ranges from 16-22 inches annually.
Associated sites
R047XA002UT Semi-moist Streambank (narrowleaf cottonwood)
Sites often occur adjacent to each other.
Similar sites
R047XA416UT Mountain Loamy Bottom (basin big sagebrush)
Table 1. Dominant plant species
Tree Not specified
Shrub (1) Artemisia tridentata ssp. tridentata
Herbaceous (1) Leymus cinereus
Physiographic features
This ecological site typically occurs on canyon floors. Slopes normally range from 0 to 8 percent but may occasionally be steeper. Sites are typically located between 5,600 to 8,800 feet in elevation. Runoff is low to medium.
Table 2. Representative physiographic features
Landforms (1) Canyon
Runoff class Low to medium Flooding duration Very brief (4 to 48 hours) Flooding frequency None to occasional Ponding frequency None Elevation 5600 – 8800 ft Slope 0 – 8 % Aspect Aspect is not a significant factor Climatic features
The climate of this site characterized by cold, snowy winters and cool summers. The average annual precipitation ranges from 16 to 22 inches. March thru May and August, are typically the wettest months with June and July being the driest. The most reliable sources of moisture for plant growth are the snow that accumulates over the winter, and spring rains. Summer thunderstorms are intermittent and sporadic in nature, and thus, are less reliable sources of moisture to support vegetative growth on this site.
Table 3 Representative climatic features
Frost-free period (characteristic range) 70-100 days Freeze-free period (characteristic range) Precipitation total (characteristic range) 20-20 in ">Influencing water features
This site is found in low-lying areas and is often adjacent to streams.
Wetland description
Further review is required.
Soil features
The soils of this site formed mostly in alluvium from andesite, dacite, basalt, or tuff.. Surface soils are very dark grayinsh brown and cobbly sandy loam in texture. Rock fragments may be present on the soil surface and throughout the profile, but make up less than 35 percent of the soil volume. These soils are deep to very deep, moderately well-drained, and have moderately permeability. pH is neutral. Available water-holding capacity ranges from 3 to 5.2 inches of water in the upper 60 inches of soil. The soil moisture regime is mostly xeric and the soil temperature regime is frigid.
Table 4. Representative soil features
Parent material (1) Alluvium – andesite
(2) Alluvium – dacite
(3) Alluvium – basalt
Surface texture (1) Cobbly sandy loam
Family particle size (1) Loamy-skeletal
Drainage class Moderately well drained Permeability class Moderate Depth to restrictive layer 60 in Soil depth 60 in Surface fragment cover <=3" 15 % Surface fragment cover >3" 20 % Available water capacity
(0-40in)3 – 5.2 in Calcium carbonate equivalent
(0-40in)Not specified Electrical conductivity
(0-40in)Not specified Sodium adsorption ratio
(0-40in)Not specified Subsurface fragment volume <=3"
(0-40in)22 % Subsurface fragment volume >3"
(0-40in)20 % Ecological dynamics
Historic vegetation on this site was dominated by tall (7ft) cool season grasses, which are adapted to occasional high water tables. Other significant vegetation includes a variety of forbs and shrubs.
The dominant aspect of this site was grasses. The composition and production will vary naturally due to location (north to south of the MLRA), fluctuating precipitation, and fire return interval.
Due to the abundant forage, thermal cover, and often close proximity to water sources, this site has a high probability of receiving grazing pressures from domestic and wildlife grazers as well as having received historical grazing pressure.
Great basin wildrye is sensitive to spring grazing and clipping and frequent herbage removal during the growing season (Perry and Chapman 1976). Thus, under repetitive harvesting, Great basin wildrye can be “grazed out” of the system. As ecological condition deteriorates due to improper grazing, cool season grasses Great basin wildrye and Nevada bluegrass decrease in frequency and production. The ungrazed plants or grazing tolerant plants such as Basin big sagebrush, rabbitbrush and other will increase in frequency and production. This increase combined with the declining perennial grasses can lead to a site dominated by sagebrush and rabbitbrush with little to no understory. The area without an understory of perennial grasses and forbs has little value as a functioning ecosystem.
As a result of the grass dominated system, this site had lots of root mass and vegetation production which creates and maintains an organic layer and a mollic epipedon. If the perennial grasses are removed from the system, it is typical to see a decrease in organic matter and accelerated erosion.
Great Basin wildrye is also susceptible to Black grass bugs. Black grass bugs populations will invade a site, and can destroy most of the living grasses.
The fire regime for this site is similar to the surrounding sagebrush lands. The intensity of a fire determines the vegetation succession and structure. Low intensity or ground fires typically result in the removal of litter and decadent grasses while maintaining the nominal shrub cover, while higher intensity fires will remove the shrub species. After normal to high intensity fires, basin big sagebrush decreases while rubber rabbitbrush increases. If the fire regime is suppressed, this site may be invaded by Junipers.
Because of the position on the landscape, this site is typically one of the first to be invaded. Junipers will start to creep down into the sagebrush lands by using this site as a corridor. The fire transition stages are relatively short lived and tend to be mosaic in nature.
If thistles, houndstounge or other strongly invasive species invade the site concurrent to the area being stressed though disturbances or drought they are likely to invade and dominate this site.
When more information is available, this section will include a discussion of seral stages; fire influence and effects; effects of prolonged wet or dry periods; resistance to change; the influence of such things as grazing, rodent concentrations, insects, diseases, introduced species, and soil erosion or deposition; other stable vegetative states associated with this site as a result of extreme disturbance.State and transition model
Custom diagramStandard diagram
More interactive model formats are also available. View Interactive Models
More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective textEcosystem states
T1a - Improper grazing and drought T2a - Long-term improper grazing and prolonged drought; lengthened fire return interval T2b - Sustained, long-term improper grazing and prolonged drought; shortened fire frequency R3a - mechanical or chemical brush treatments State 1 submodel, plant communities
1.1b - Recent fire occurrence (1 to 30 years). 1.1a - Extended period of time with no major disturbance 1.2a - Normalized or extended fire frequency 1.3a - Recent fire occurrence (1 to 30 years). State 2 submodel, plant communities
2.1b - Recent fire occurrence (1 to 30 years). 2.1a - Extended period of time without a major disturbance such as fire 2.2a - 40 to 50 years or more without a fire occurrence (normal fire frequency). 2.3a - Recent fire occurrence (1 to 30 years). State 3 submodel, plant communities
3.1a - Long-term improper grazing and drought 3.2a - Proper grazing management State 4 submodel, plant communities
4.1a - Long-term, improper grazing and drought 4.2a - properly grazed for an extended period of time State 5 submodel, plant communities
5.1a - Long-term improper grazing and drought 5.2a - properly grazed over an extended period of time State 1
Reference StateCommunity 1.1
Basin big sagebrush / Rubber rabbitbrush Great basin wildrye / Western wheatgrass Longleaf Hawksbeard / Arrowleaf BalsamrootThis community is dominated by Great basin wildrye. Basin big sagebrush is the major shrub. Other significant herbaceous species in the plant community include western wheatgrass, Nevada bluegrass, longleaf hawksbeard and arrowleaf balsamroot. Rubber rabbitbrush and Black greasewood are other important shrubs. Percent composition by air-dry weight is 70 percent grass, 10 percent forbs, and 20 percent shrubs. Natural fire frequency is estimated to be 40 to 50 years.
Community 1.2
Great basin wildrye / Western wheatgrass Yellow rabbitbrush / GreasewoodBasin big sagebrush decreases in the community; rubber rabbitbrush also decreases, but to a lesser degree. Yellow rabbitbrush, black greasewood and, at times, horsebrush species re-sprout and increase in the community; much of the excess fine fuel accumulation is removed. Basin wildrye and other cool season bunchgrasses recover following fire and flourish, Western wheatgrass increases. Fire tolerant shrubs may persist as dominants in the shrub community for 30 years or longer.
Community 1.3
Basin big sagebrush / Rubber rabbitbrush /Greasewood / perennial grassesBasin big sagebrush, rubber rabbitbrush and black greasewood increase in percent composition. Shrubs show signs of decadence due to age. Great basin wildrye and other cool season bunchgrasses begin loosing vigor due to increased shrub competition and increase in old vegetation. Percent composition by air-dry weight is 40 percent grass, 10 percent forbs, and 50 percent shrubs.
Pathway 1.1b
Community 1.1 to 1.2Disturbance: Recent fire occurrence (1 to 30 years).
Pathway 1.1a
Community 1.1 to 1.3Extended period of time without a major disturbance such as fire; insect infestation (i.e. black grass bugs); or prolonged drought. Fire frequency extends well beyond the 40 to 50 year average for the site.
Pathway 1.2a
Community 1.2 to 1.140 to 50 years or more without a fire occurrence (normal fire frequency).
Pathway 1.3a
Community 1.3 to 1.2Disturbance: Recent fire occurrence (1 to 30 years).
State 2
Current Potential StatePlant communities in this state can include native, acclimatized, naturalized and invasive non-native species. This state is irreversibly changed from the Reference State because these non-native species will now remain a permanent part of the community.
Community 2.1
Basin big sagebrush / Rubber rabbitbrush Great basin wildrye / Western wheatgrass Longleaf Hawksbeard / Arrowleaf Balsamroot Non-native speciesThis community is dominated by Great basin wildrye. Basin big sagebrush is the major shrub. Other significant herbaceous species in the plant community include western wheatgrass, Nevada bluegrass, longleaf hawksbeard and arrowleaf balsamroot. Rubber rabbitbrush and black greasewood are other important shrubs. This community is dominated by native species, but may include acclimatized, naturalized and invasive non-native species. Percent composition by air-dry weight is 70 percent grass, 10 percent forbs, and 20 percent shrubs.
Community 2.2
Great basin wildrye / Western wheatgrass Yellow rabbitbrush / Greasewood Non-native speciesBasin big sagebrush decreases in the community; rubber rabbitbrush also decreases, but to a lesser degree. Yellow rabbitbrush, Black greasewood and, at times, horsebrush species re-sprout and increase in the community; much of the excess fine fuel accumulation is removed. Basin wildrye and other cool season bunchgrasses recover following fire and flourish, Western wheatgrass increases. Fire tolerant shrubs may persist as dominants in the shrub community for 30 years or longer. This community is dominated by native species, but may include acclimatized, naturalized and invasive non-native species.
Community 2.3
Basin big sagebrush / Rubber rabbitbrush /Greasewood / perennial grasses Non-native speciesPathway 2.1b
Community 2.1 to 2.2Recent fire occurrence (1 to 30 years).
Pathway 2.1a
Community 2.1 to 2.3Extended period of time without a major disturbance such as fire; insect infestation (i.e. black grass bugs); or prolonged drought. Fire frequency extends well beyond the 40 to 50 year average for the site.
Pathway 2.2a
Community 2.2 to 2.140 to 50 years or more without a fire occurrence (normal fire frequency).
Pathway 2.3a
Community 2.3 to 2.2Recent fire occurrence (1 to 30 years).
State 3
Utah Juniper, Brush with Annual Weeds StateCommunity 3.1
Basin big sagebrush and Utah juniper Invasive annuals / Native perennialsWhere Utah juniper has invaded, basin big sagebrush, rubber rabbitbrush and black greasewood may decrease, otherwise they dominate the community; yellow rabbitbrush often increases. Remaining perennial herbaceous vegetation is mostly found only in protected locations under shrubs. Invasive, non-native grasses and weeds, including cheatgrass, annual mustards, redstem storksbill, etc. dominate the understory.
Community 3.2
Basin big sagebrush and Utah juniper Invasive annualsWhere Utah juniper has invaded, basin big sagebrush, rubber rabbitbrush, and black greasewood decrease, otherwise they may dominate the community; yellow rabbitbrush often increases. Remaining perennial herbaceous vegetation is rare and is found only in protected locations under shrubs. Invasive, non-native grasses and weeds, including cheatgrass, annual mustards, redstem storksbill, etc., dominate the understory.
Pathway 3.1a
Community 3.1 to 3.2Disturbance: Long-term improper grazing (including, season long, overstocking, wrong season, etc.) and drought reduce perennial grasses. Fine fuels are reduced lessening the potential for fire to occur. Fire frequency is greater than 100 years.
Pathway 3.2a
Community 3.2 to 3.1Site is properly grazed over an extended period of time. Native perennial vegetation slowly recovers; annual weeds dominate the understory. Fire frequency remains well beyond normal for the site. Fire frequency is greater than 100 years.
State 4
Sprouting Shrub with Annual Weeds StateCommunity 4.1
Rabbitbrushes / Greasewood Invasive annuals / Native perennialsYellow rabbitbrush, black greasewood and smooth horsebrush re-sprout and dominate the shrub layer. Rubber rabbitbrush can be plentiful if conditions are right.
Fire tolerant shrubs may persist as dominants with fire periods of 10 to 30 years.
Broom snakeweed may be an episodic dominant species when conditions are favorable. Native bunchgrasses are significantly reduced; invasive annuals including cheatgrass, annual mustards, redstem storksbill, etc. dominate the understory.Community 4.2
Rabbitbrushes / Greasewood Invasive annualsYellow rabbitbrush, black greasewood and smooth horsebrush dominate the overstory community. Rubber rabbitbrush can be plentiful if conditions are right.
Fire tolerant shrubs may persist as dominants in this community with fire periods of 10 to 30 years. Broom snakeweed may be an episodic dominant species when conditions are favorable. Only remnant native bunchgrasses remain; invasive annuals including cheatgrass, annual mustards, redstem storksbill, etc. dominate the understory.Pathway 4.1a
Community 4.1 to 4.2Disturbance: Long-term, improper grazing (including, season long, overstocking, wrong season, etc.) and drought reduce perennial grasses. Highly combustible fine fuels from invasive annuals dominate the community resulting in a shortened fire frequency. Fire frequency is typically 10 to 30 years.
Pathway 4.2a
Community 4.2 to 4.1Site is properly grazed for an extended period of time. Perennial vegetation very slowly recovers. Fire frequency is typically 10 to 30 years.
State 5
Seeded Rangeland StateCommunity 5.1
Basin big sagebrush and\or Utah juniper Invasive annuals / Non-Native perennialsRangeland seeding that may be composed of introduced, native or combination grass and forb species. Unwanted trees and shrubs are reduced but may occupy a portion of the site because of natural regeneration. Invasive annual grasses and weedy forb species, primarily cheatgrass and various annual mustards, may be present in the seeding. Seeding, when healthy, is resistant to fire.
Community 5.2
Basin big sagebrush and/or Utah juniper Invasive annualsThis state is present after either a failed seeding or an improperly grazed one. Site may be herbaceous or may be returning to trees and/or shrubs.
Pathway 5.1a
Community 5.1 to 5.2Disturbance: Long-term improper grazing (including, season long, overstocking, wrong season, etc.) and drought reduce perennial grasses. Fine fuels are reduced lessening the potential for fire to occur. Fire frequency is greater than 100 years.
Pathway 5.2a
Community 5.2 to 5.1Site is properly grazed over an extended period of time. Native perennial vegetation slowly recovers; annual weeds dominate the understory. Fire frequency remains well beyond normal for the site. Fire frequency is greater than 100 years.
State 6
Cropland StateThis state occurs when the Loamy Bottom ecological site is altered and permanently replaced with agricultural crops such as alfalfa and grain. This State is identified here to recognize that a very large portion of this ecological site has been converted to a cropland land use.
Transition T1a
State 1 to 2Improper grazing (i.e. season long, overstocking, wrong season, etc.) and drought remove fine fuels from the site lessening the potential for fire to occur. This allows both sprouting and non-sprouting shrubs such as basin big sagebrush, rubber rabbitbrush and black greasewood to increase in the community. Shrubs may become decadent due to age. Great basin wildrye and other native bunchgrasses lose vigor and decrease in the community due to shrub competition and grazing pressure; western wheatgrass may increase. Utah juniper seedlings and saplings may begin to invade the community if a seed source is available. The threshold is crossed when there is an introduction of non-native species, primarily cheatgrass and various annual mustards, that become established on the site. Prior to crossing the threshold, if this site is properly grazed over an extended period of time native perennial vegetation may recover. Fire frequency can return to within the normal range for the site. These events could set the site back into the normal range of variability.
Transition T2a
State 2 to 3Long-term improper grazing (including, season long, overstocking, wrong season, etc.); and prolonged drought; lengthened fire return interval resulting in a dense non-sprouting tree and shrub overstory, reduction of native perennial understory vegetation and increasing invading annuals. Utah junipers may increase to occupy a significant portion of the overstory, if a seed source is present. Basin big sagebrush dominates the shrub layer and may be decadent due to age. Rubber rabbitbrush and Greasewood may also be present. Great basin wildrye and other native bunchgrasses are significantly reduced due to increased shrub competition and heavy grazing pressure; Western wheatgrass may increase. The threshold is crossed when invasive annuals including cheatgrass, annual mustards, redstem storksbill, etc. dominate the understory. The occurrence of fire extends well beyond the normal period for the site.
Transition T2b
State 2 to 4Disturbance: Sustained, long-term improper grazing (including, season long, overstocking, wrong season, etc.) and prolonged drought; shortened fire frequency allows site to be dominated by sprouting shrubs including Yellow rabbitbrush, Black greasewood and Smooth horsebrush; significant reduction of perennial bunchgrass species. There is an invasion of annual grasses and weedy forb species primarily cheatgrass and various annual mustards.
Restoration pathway R3a
State 3 to 5Disturbance: Mechanical chaining of Utah juniper where present, or mechanical or chemical treatment of unwanted brush species; with seeding of introduced, native or combination rangeland species.
Additional community tables
Table 5. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 6. Community 1.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 7. Community 1.3 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 8. Community 2.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 9. Community 2.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 10. Community 2.3 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 11. Community 3.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 12. Community 3.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 13. Community 4.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 14. Community 4.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 15. Community 5.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 16. Community 5.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Interpretations
Supporting information
Inventory data references
Information presented here has been derived from NRCS clipping data and other inventory data. Field observations from range trained personnel were also used.
Other references
Alexander, R. R. 1985. Major habitat types, community types, and plant communities in the Rocky Mountains. USDA- Forest Service Rocky Mountain Forest and Range Experiment Station. General technical report RM-123. 105p.
Alexander 1988. Forest vegetation on National Forests in the Rocky Mountain and Intermountain Regions: Habitat types and community types. USDA- Forest Service Rocky Mountain Forest and Range Experiment Station. General technical report RM-162. 47p.
Galatowitsch, S.M. 1990. Using the original land survey notes to reconstruct pre-settlement landscapes in the American West. Great Basin Naturalist: 50(2): 181-191. Keywords: [Western U.S., conservation, history, human impact]
Parson, R. E. 1996. A History of Rich County. Utah State Historical Society, County Commission, Rich County, Utah. Keywords: [Rich County, Utah, Historic land use, European settlements]
USDA-NRCS. 2003. National Range and Pasture Handbook. in USDA, editor, USDA-Natural Resources Conservation Service-Grazing Lands Technology Institute. Keywords: [Western US, Federal guidelines, Range pasture management]
Western Regional Climate Center, Western U.S. Climate Historical Summaries. Available at: http://www.wrcc.dri.edu/summary/Climsmut.html. Accessed 15 June 2009.
Web Soil Survey, Official Soil Series Descriptions. Available at: http://soils.usda.gov/technical/classification/osd/index.html. Accessed 15 June 2009.Contributors
Jamin Johanson, NRCS
Shane Green, NRCS
M. Dean Stacy, NRCSApproval
Kendra Moseley, 2/05/2025
Rangeland health reference sheet
Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.
Author(s)/participant(s) Contact for lead author Date 07/11/2026 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
-
Number and extent of rills:
-
Presence of water flow patterns:
-
Number and height of erosional pedestals or terracettes:
-
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
-
Number of gullies and erosion associated with gullies:
-
Extent of wind scoured, blowouts and/or depositional areas:
-
Amount of litter movement (describe size and distance expected to travel):
-
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
-
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
-
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
-
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
-
Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Sub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
-
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
-
Potential invasive (including noxious) species (native and non-native). List species which BOTH characterize degraded states and have the potential to become a dominant or co-dominant species on the ecological site if their future establishment and growth is not actively controlled by management interventions. Species that become dominant for only one to several years (e.g., short-term response to drought or wildfire) are not invasive plants. Note that unlike other indicators, we are describing what is NOT expected in the reference state for the ecological site:
-
Perennial plant reproductive capability:
Print Options
Sections
Font
AAAAOther
PrintThe Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
Accessibility statement
