
Natural Resources
Conservation Service
Ecological site R023XY007NV
LOAMY 14-16 P.Z.
Last updated: 4/10/2025
Accessed: 04/12/2025
General 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.
Associated sites
R023XY017NV |
CLAYPAN 14-16 P.Z. |
---|---|
R023XY019NV |
LOAMY 16+ P.Z. |
R023XY066NV |
ASHY LOAM 14-16 P.Z. |
Similar sites
R023XY041NV |
LOAMY 12-14 P.Z. PSSPS-LECI4 codominant |
---|---|
R023XY072NV |
ASHY SLOPE 10-12 P.Z. FEID dominant grass; ARTRW8 dominant shrub |
R023XY066NV |
ASHY LOAM 14-16 P.Z. FEID dominant grass |
R023XY071NV |
ASHY LOAM 10-12 P.Z. FEID dominant grass; ARTRT dominant shrub |
R023XY019NV |
LOAMY 16+ P.Z. BRMA4 and ACHNA dominant grasses; more productive site; higher amount of mountain browse spp. |
Table 1. Dominant plant species
Tree |
Not specified |
---|---|
Shrub |
(1) Artemisia tridentata var. vaseyana |
Herbaceous |
(1) Festuca idahoensis |
Physiographic features
This site occurs on summits and sideslopes of plateaus, hills, and mountains on all aspects. At lower elevations this site is restricted to cool, moist, northerly exposures. Slopes range from 4 to 75 percent, but slope gradients of 15 to 50 percent are most typical. Elevations are 5000 to 7800 feet.
Table 2. Representative physiographic features
Landforms |
(1)
Mountain slope
(2) Plateau |
---|---|
Elevation | 1,524 – 2,377 m |
Slope | 4 – 75% |
Aspect | Aspect is not a significant factor |
Climatic features
The climate associated with this site is semiarid and characterized by cool, moist winters and warm, dry summers. Average annual precipitation is 12 to 16 inches. Mean annual air temperature is 45 to 50 degrees F. The average growing season is about 60 to 90 days.
Nevada’s climate is predominantly arid, with large daily ranges of temperature, infrequent severe storms, heavy snowfall in the higher mountains, and great location variations with elevation. Three basic geographical factors largely influence Nevada’s climate: continentality, latitude, and elevation. Continentality is the most important factor. The strong continental effect is expressed in the form of both dryness and large temperature variations. Nevada lies on the eastern, lee side of the Sierra Nevada Range, a massive mountain barrier that markedly influences the climate of the State. The prevailing winds are from the west, and as the warm moist air from the Pacific Ocean ascend the western slopes of the Sierra Range, the air cools, condensation occurs and most of the moisture falls as precipitation. As the air descends the eastern slope, it is warmed by compression, and very little precipitation occurs. The effects of this mountain barrier are felt not only in the West but throughout the state, with the result that the lowlands of Nevada are largely desert or steppes. The temperature regime is also affected by the blocking of the inland-moving maritime air. Nevada sheltered from maritime winds, has a continental climate with well-developed seasons and the terrain responds quickly to changes in solar heating.
Nevada lies within the mid-latitude belt of prevailing westerly winds which occur most of the year. These winds bring frequent changes in weather during the late fall, winter and spring months, when most of the precipitation occurs. To the south of the mid-latitude westerlies, lies a zone of high pressure in subtropical latitudes, with a center over the Pacific Ocean. In the summer, this high-pressure belt shifts northward over the latitudes of Nevada, blocking storms from the ocean. The resulting weather is mostly clear and dry during the summer and early fall, with scattered thundershowers. The eastern portion of the state receives significant summer thunderstorms generated from monsoonal moisture pushed up from the Gulf of California, known as the North American monsoon. The monsoon system peaks in August and by October the monsoon high over the Western U.S. begins to weaken and the precipitation retreats southward towards the tropics (NOAA 2004).
Average annual precipitation is 16 to over 20 inches. Mean annual air temperature is 41 to 44 degrees F. The average growing season is about 50 to 70 days.
Mean annual precipitaion at the Bear Creek, Nevada SNOTEL station (170501020301) is 37.69 inches.
monthly mean precipitation is:
January 3.84; February 3.75; March 4.38; April 4.9;
May 3.99; June 2.82; July .95; August 1.66;
September 1.22; October 2.12;
November 3.67; December 4.38.
Table 3. Representative climatic features
Frost-free period (average) | 75 days |
---|---|
Freeze-free period (average) | |
Precipitation total (average) | 356 mm |
Figure 1. Monthly precipitation range
Figure 2. Monthly average minimum and maximum temperature
Figure 3. Annual precipitation pattern
Figure 4. Annual average temperature pattern
Influencing water features
There are no influencing water features associated with this site.
Soil features
The soils associated with this site are formed in volcanic ash, residuum and colluvium derived from volcanic rocks. The soils are moderately deep to very deep and are well drained. These soils have thick, dark-colored, loamy surface layers and subsoils are friable loams, clay loams, or clays. Soils are neutral to slightly acid and non-calcareous. Sheet and rill erosion potential is slight to moderate depending on slope. Few overland flow patterns are discernible. Wind erosion potential is slight. The soils have a thick mollic epipedon and an argillic horizon. The soil temperature regime is aridic bordering on xeric and the soil temperature regime is frigid. The soil series associated with this site includes: Alyan, Home Camp, Menbo, Newlands, Pearlwise, Softscrabble, Tusk, and Westbutte.
A representative soil seris is Menbo, a clayey-skeletal, smectitic, frigid Vitrandic Argixerolls. A mollic epipedon occurs from the soil surface to 66 cm and an argillic horizon occurs from 20 to 66 cm.
Table 4. Representative soil features
Parent material |
(1)
Colluvium
–
basalt
(2) Residuum – andesite |
---|---|
Surface texture |
(1) Ashy loam (2) Gravelly loam |
Family particle size |
(1) Clayey |
Drainage class | Well drained |
Permeability class | Slow to moderate |
Soil depth | 102 – 213 cm |
Surface fragment cover <=3" | 4 – 50% |
Surface fragment cover >3" | 3 – 25% |
Available water capacity (0-101.6cm) |
10.16 – 16.51 cm |
Calcium carbonate equivalent (0-101.6cm) |
0% |
Electrical conductivity (0-101.6cm) |
0 mmhos/cm |
Sodium adsorption ratio (0-101.6cm) |
0 |
Soil reaction (1:1 water) (0-101.6cm) |
6.1 – 7.8 |
Subsurface fragment volume <=3" (Depth not specified) |
9 – 30% |
Subsurface fragment volume >3" (Depth not specified) |
5 – 40% |
Ecological dynamics
Where management results in abusive grazing use by livestockand/or feral horses, mountain big sagebrush and rabbitbrush will increase at the expense of Idaho fescue and bluebunch wheatgrass. Moderate to heavy sheep use of this site will decrease abundance of Idaho fescue, needlegrass and bluegrasses. Heavy, early season, cattle or horse use will decrease bluebunch wheatgrass composition in the community. Cheatgrass, mustards, and thistle are plant species most likely to invade this site.
Fire Ecology:
Presettlement fire return intervals in mountain big sagebrush communities varied from 15 to 25 years. Plants are readily killed in all seasons, even light severity fires. Mountain big sagebrush is highly susceptible to injury from fire. It is often top-killed by fire and will not resprout. Antelope bitterbrush is considered a weak sprouter and is often killed by summer or fall fire. Antelope bitterbrush in some areas may sprout after light-severity spring fire. High fuel consumptions increase antelope bitterbrush mortality and therefore favors seedling establishment. Idaho fescue grows in a dense, fine-leaved tuft. Fires tend to burn within the accumulated fine leaves at the base of the plant and may produce temperatures sufficient to kill some of the root crown. Mature Idaho fescue plants are commonly reported to be severely damaged by fire in all seasons. Burning bluebunch wheatgrass may remove most of the aboveground biomass but does not usually result in plant mortality. Bluebunch wheatgrass is generally favored by burning. Burning stimulates flowering and seed production. However, season of burning affects mortality. Basin wildrye is top-killed by fire. Older basin wildrye plants with large proportions of dead material within the perennial crown can be expected to show higher mortality due to fire than younger plants having little debris. Basin wildrye is generally tolerant of fire but may be damaged by early season fire combined with dry soil conditions. Western needlegrass is moderately damaged by fire. The recovery time is between 3 and 5 years. Thurber’s needlegrass is classified as moderately resistant, but depending on season of burn, phenology, and fire severity, this perennial bunchgrass is moderately to severely damaged by fire. Burning has been found to decrease the vegetation and reproductive vigor. Early season burning is more damaging to this needlegrass than late season burning. Canby's bluegrass is generally unharmed by fire. It produces little litter, and its small bunch size and sparse litter reduces the amount of heat transferred to perennating buds in the soil. Its rapid maturation in the spring also reduces fire damage, since it is dormant when most fires occur. Cusick’s bluegrass is unharmed to slightly harmed by light-severity fall fires. Cusick’s bluegrass regenerates after fire from seed and by tillering.
State and transition model
More interactive model formats are also available.
View Interactive Models
Click on state and transition labels to scroll to the respective text
Ecosystem states
States 2 and 5 (additional transitions)
State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 5 submodel, plant communities
State 1
Reference State
Community 1.1
Community Phase
The reference plant community is dominated by bluebunch wheatgrass, Idaho fescue and mountain big sagebrush. Potential vegetative composition is about 60% grasses, 10% forbs and 30% shrubs. Approximate ground cover (basal and crown) is about 30 to 45 percent.
Figure 5. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
---|---|---|---|
Grass/Grasslike | 605 | 807 | 1076 |
Shrub/Vine | 303 | 404 | 538 |
Forb | 101 | 135 | 179 |
Total | 1009 | 1346 | 1793 |
Community 1.2
Community Phase
Community 1.3
Community Phase
Pathway a
Community 1.1 to 1.2
Pathway b
Community 1.1 to 1.3
Pathway a
Community 1.2 to 1.1
Pathway a
Community 1.3 to 1.1
Pathway b
Community 1.3 to 1.2
State 2
Current Potential State
Community 2.1
Community Phase
Community 2.2
Community Phase
Community 2.3
Community Phase (at risk)
Community 2.4
Community Phase (at risk)
Pathway a
Community 2.1 to 2.2
Pathway b
Community 2.1 to 2.3
Pathway c
Community 2.1 to 2.4
Pathway a
Community 2.2 to 2.1
Pathway b
Community 2.2 to 2.4
Pathway a
Community 2.3 to 2.1
Pathway b
Community 2.3 to 2.2
Pathway a
Community 2.4 to 2.1
Pathway b
Community 2.4 to 2.2
State 3
Sagebrush State
Community 3.1
Community Phase
Community 3.2
Community Phase
Pathway a
Community 3.1 to 3.2
Pathway a
Community 3.2 to 3.1
State 4
Tree State
Community 4.1
Community Phase
Community 4.2
Community Phase
Pathway a
Community 4.1 to 4.2
State 5
Annual State
Community 5.1
Community Phase
Community 5.2
Community Phase
Pathway a
Community 5.1 to 5.2
Pathway a
Community 5.2 to 5.1
Transition A
State 1 to 2
Transition A
State 2 to 3
Transition B
State 2 to 4
Transition C
State 2 to 5
Restoration pathway A
State 3 to 2
Transition A
State 3 to 4
Transition B
State 3 to 5
Restoration pathway A
State 4 to 2
Restoration pathway B
State 4 to 3
Transition A
State 4 to 5
Additional community tables
Table 6. Community 1.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | Primary Perennial Grasses | 861–1480 | ||||
Idaho fescue | FEID | Festuca idahoensis | 404–538 | – | ||
bluebunch wheatgrass | PSSPS | Pseudoroegneria spicata ssp. spicata | 336–538 | – | ||
basin wildrye | LECI4 | Leymus cinereus | 27–135 | – | ||
western needlegrass | ACOCO | Achnatherum occidentale ssp. occidentale | 34–101 | – | ||
Thurber's needlegrass | ACTH7 | Achnatherum thurberianum | 34–101 | – | ||
Cusick's bluegrass | POCUE2 | Poa cusickii ssp. epilis | 13–34 | – | ||
2 | Secondary Perennial Grasses | 27–108 | ||||
mountain brome | BRMA4 | Bromus marginatus | 7–40 | – | ||
sedge | CAREX | Carex | 7–40 | – | ||
prairie Junegrass | KOMA | Koeleria macrantha | 7–40 | – | ||
Forb
|
||||||
3 | Perennial | 67–202 | ||||
arrowleaf balsamroot | BASA3 | Balsamorhiza sagittata | 3–40 | – | ||
tapertip hawksbeard | CRAC2 | Crepis acuminata | 3–40 | – | ||
western stoneseed | LIRU4 | Lithospermum ruderale | 3–40 | – | ||
desertparsley | LOMAT | Lomatium | 3–40 | – | ||
lupine | LUPIN | Lupinus | 3–40 | – | ||
Shrub/Vine
|
||||||
4 | Primary Shrubs | 161–404 | ||||
mountain big sagebrush | ARTRV | Artemisia tridentata ssp. vaseyana | 135–269 | – | ||
antelope bitterbrush | PUTR2 | Purshia tridentata | 27–135 | – | ||
5 | Secondary Shrubs | 67–202 | ||||
Utah serviceberry | AMUT | Amelanchier utahensis | 13–67 | – | ||
curl-leaf mountain mahogany | CELE3 | Cercocarpus ledifolius | 13–67 | – | ||
yellow rabbitbrush | CHVI8 | Chrysothamnus viscidiflorus | 13–67 | – | ||
currant | RIBES | Ribes | 13–67 | – | ||
mountain snowberry | SYOR2 | Symphoricarpos oreophilus | 13–67 | – |
Interpretations
Animal community
Livestock Interpretations:
This site is suitable for grazing. Grazing management should be keyed to perennial grass production. Idaho fescue provides important forge for many types of domestic livestock. The foliage cures well and is preferred by livestock in late fall and winter. Bluebunch wheatgrass is considered one of the most important forage grass species on western rangelands for livestock. Although bluebunch wheatgrass can be a crucial source of forage, it is not necessarily the most highly preferred species. The early growth and abundant production of basin wildrye make it a valuable source of forage for livestock. It is important forage for cattle and is readily grazed by cattle and horses in early spring and fall. Though coarse-textured during the winter, basin wildrye may be utilized more frequently by livestock and wildlife when snow has covered low shrubs and other grasses. Western needlegrass has a spreading and deeply penetrating root system, which makes it resistant to trampling. Thurber’s needlegrass begins growth early in the year and remain green throughout a relatively long growing season. This pattern of development enables animals to use Thurber’s needlegrass when many other grasses are unavailable. Cattle prefer Thurber’s needlegrass in early spring before fruits have developed as it becomes less palatable when mature. Thurber’s needlegrasses are grazed in the fall only if the fruits are softened by rain. Canby's bluegrass is a widespread forage grass. It is one of the earliest grasses in the spring and is sought by domestic livestock and several wildlife species. Canby's bluegrass is a palatable species, but its production is closely tied to weather conditions. It produces little forage in drought years, making it a less dependable food source than other perennial bunchgrasses. Cusick's bluegrass makes up only a small proportion of the biomass of the sagebrush communities in which it lives, but it is often taken preferentially by cattle, especially early in the season. Mountain big sagebrush is eaten by domestic livestock but has long been considered to be of low palatability, and a competitor to more desirable species. Antelope bitterbrush is important browse for livestock. Domestic livestock and mule deer may compete for antelope bitterbrush in late summer, fall, and/or winter. Cattle prefer antelope bitterbrush from mid-May through June and again in September and October.
Stocking rates vary over time depending upon season of use, climate variations, site, and previous and current management goals. A safe starting stocking rate is an estimated stocking rate that is fine tuned by the client by adaptive management through the year and from year to year.
Wildlife Interpretations:
Mountain big sagebrush is highly preferred and nutritious winter forage for mule deer and elk. Sagebrush-grassland communities provide critical sage-grouse breeding and nesting habitats. Meadows surrounded by sagebrush may be used as feeding and strutting grounds. Sagebrush is a crucial component of their diet year-round, and sage-grouse select sagebrush almost exclusively for cover. Sage-grouse prefer mountain big sagebrush and Wyoming big sagebrush communities to basin big sagebrush communities. Pronghorn antelope, mule deer, elk, and bighorn sheep utilize antelope bitterbrush extensively. Mule deer use of antelope bitterbrush peaks in September, when antelope bitterbrush may compose 91 percent of the diet. Winter use is greatest during periods of deep snow. Antelope bitterbrush seed is a large part of the diets of rodents, especially deer mice and kangaroo rats. Idaho fescue provides important forge for several wildlife species. It is reported to be good forage for pronghorn, and deer in ranges of northern Nevada. Bluebunch wheatgrass is considered one of the most important forage grass species on western rangelands for wildlife. Bluebunch wheatgrass does not generally provide sufficient cover for ungulates, however, mule deer are frequently found in bluebunch-dominated grasslands. Basin wildrye provides winter forage for mule deer, though use is often low compared to other native grasses. Basin wildrye provides summer forage for black-tailed jackrabbits. Because basin wildrye remains green throughout early summer, it remains available for small mammal forage for longer time than other grasses. Western needlegrass and Thurber's needlegrass provide valuable forage for many species of wildlife. Canby's bluegrass is desirable for pronghorn antelope and mule deer in the spring and preferable in the spring, summer, and fall for elk and desirable as part of their winter range. Deer, elk, and mountain goat also use Cusick's bluegrass early in the season. The value of Cusick's bluegrass as cover for small animals has been rated as poor to fair.
Hydrological functions
There are typically no rills. There may be a few, widely spaced and shallow, rills on steeper slopes (over 20% gradient). Water flow patterns are typically non-existent but can rarely occur on steeper slopes in areas recently subjected to intense summer convection storms or rapid snowmelt. Pedestals are typically non-existent. Frost heaving of shallow rooted plants should not be considered a "normal" condition. Gullies are non-existent in areas of this site that occur on stable landforms. Perennial herbaceous plants (especially deep-rooted bunchgrasses [i.e., bluebunch wheatgrass] slow runoff and increase infiltration. Shrub canopy and associated litter break raindrop impact and provide opportunity for snow catch and accumulation on site.
Recreational uses
Aesthetic value is derived from the diverse floral and faunal composition and the colorful flowering of wild flowers and shrubs during the spring and early summer. This site offers rewarding opportunities to photographers and for nature study. This site is used for camping and hiking and has potential for upland and big game hunting.
Other products
Native Americans used big sagebrush leaves and branches for medicinal teas, and the leaves as a fumigant. Bark was woven into mats, bags and clothing. Basin wildrye was used as bedding for various Native American ceremonies, providing a cool place for dancers to stand.
Other information
Antelope bitterbrush has been used extensively in land reclamation. Antelope bitterbrush enhances succession by retaining soil and depositing organic material and in some habitats and with some ecotypes, by fixing nitrogen. Basin wildrye is useful in mine reclamation, fire rehabilitation and stabilizing disturbed areas. Its usefulness in range seeding, however, may be limited by initially weak stand establishment.
Supporting information
Type locality
Location 1: Humboldt County, NV | |
---|---|
Township/Range/Section | T41N R26E S5 |
Latitude | 41° 29′ 31″ |
Longitude | 119° 1′ 52″ |
General legal description | NE1/4, Summit Lake Indian Reservation, Humboldt County, Nevada. This site also occurs in Washoe County, Nevada. |
Location 2: Washoe County, NV | |
Township/Range/Section | T35N R18E S33 |
Latitude | 40° 51′ 52″ |
Longitude | 119° 58′ 0″ |
General legal description | East of Pilgram Lake, Washoe County, NV. This site also occurs in Humboldt County, Nevada. |
Other references
Fire Effects Information System (Online; http://www.fs.fed.us/database/feis/plants/).
USDA-NRCS Plants Database (Online; http://www.plants.usda.gov).
Contributors
BH/SW/CP
Approval
Kendra Moseley, 4/10/2025
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) | GK BRACKLEY |
---|---|
Contact for lead author | State Rangeland Management Specialist |
Date | 06/20/2006 |
Approved by | Kendra Moseley |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
Typically none. There may be a few, widely spaced and shallow, rills on steeper slopes (over 20% gradient). -
Presence of water flow patterns:
Water flow patterns are typically non-existent but can rarely occur on steeper slopes in areas recently subjected to intense summer convection storms or rapid snowmelt. -
Number and height of erosional pedestals or terracettes:
Pedestals are typically non-existent. Frost heaving of shallow rooted plants should not be considered a "normal" condition. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare Ground ± 30%; surface rock fragments less than 50%; shrub canopy 20 to 30%; foliar cover of perennial herbaceous plants ± 40%. -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
None -
Amount of litter movement (describe size and distance expected to travel):
Fine litter (foliage from grasses and annual & perennial forbs) is expected to move the distance of slope length during intense summer convection storms or rapid snowmelt events. Persistent litter (large woody material) will remain in place except during large rainfall events. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil stability values should be 3 to 6 on most soil textures found on this site. (To be field tested.) -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Surface structure is typically subangular blocky or granular. Soil surface colors are dark browns and the soils are typified by a mollic epipedon. Organic matter of the surface 2 to 4 inches is typically 1.25 to 3 percent dropping off quickly below. Organic matter content can be more or less depending on micro-topography. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Perennial herbaceous plants (especially deep-rooted bunchgrasses [i.e., bluebunch wheatgrass] slow runoff and increase infiltration. Shrub canopy and associated litter break raindrop impact and provide opportunity for snow catch and accumulation on site. -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
Compacted layers are none. Platy or massive sub-surface horizons or subsoil argillic horizons are not to be interpreted as compacted layers. -
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:
Reference Plant Community: Deep-rooted, cool season, perennial bunchgrasses >> tall shrubs (big sagebrush & antelope bitterbrush). (By above ground production)Sub-dominant:
Associated shrubs = deep-rooted, cool season, perennial forbs > fibrous, shallow-rooted, cool season, perennial and annual forbs = shallow-rooted, cool season, perennial grasses and grass-like plants. (By above ground production)Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Dead branches within individual shrubs are common and standing dead shrub canopy material may be as much as 25% of total woody canopy; some of the mature bunchgrasses (<10%) have dead centers. -
Average percent litter cover (%) and depth ( in):
Between plant interspaces (± 35%) and litter depth is ± ½ inch. -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
For normal or average growing season (through June) ± 1200 lbs/ac; Spring moisture significantly affects total production. Favorable years ±1600 lbs/ac; unfavorable years ±900 lbs/ac. -
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:
Cheatgrass, annual mustards, knapweeds, medusahead, thistles, and Western juniper are invaders on this site. -
Perennial plant reproductive capability:
All functional groups should reproduce in average (or normal) and above average growing season years. Little growth or reproduction occurs in drought years.
Print Options
Sections
Font
Other
The 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.
Click on box and path labels to scroll to the respective text.