
Natural Resources
Conservation Service
Ecological site R023XY011NV
DUNES 8-10 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.
Ecological site concept
Currently there is only a draft of the initial concept for this ecological site. The initial concept for this site places it within the Stabilized Sand Dunes with Sagebrush and Saltbrush Ecological Site Group. To view the General STM and other information available for this ESG please go to https://edit.jornada.nmsu.edu/catalogs/esg/023X/R023XY914OR
The precipitation zone for this site ranges from 8 to 10 inches. The elevation range for this group is from 4,500 to 5,000 ft. Slopes range from 2 to 30 percent. The soils of this site are windblown, fine and very fine sands, typically more than 40 inches in depth. Soils are very susceptible to wind erosion and may have small “blow out” areas. The soil profile is excessively drained and free of salts. Because of rapid soil intake and deep percolation of water, the loss of soil moisture due to evaporation is reduced and runoff is negligible. These conditions allow deep rooted plants to grow vigorously under arid climatic conditions. The potential native plant community for this site varies depending on precipitation, elevation and landform. The shrub overstory component is dominated by basin big sagebrush (Artemisia tridentata ssp. tridentata) and spiny hopsage (Grayia spinosa). The understory is dominated by Indian ricegrass (Achnatherum hymenoides), basin wildrye (Leymus cinereus), thickspike wheatgrass (Elymus lanceolatus), and needle and thread (Hesperostipa comata). The production on this site ranges from 400 to 900 lbs/acre, with 700 lb/ac in normal years.
Associated sites
R023XY038NV |
DROUGHTY LOAM 8-10 P.Z. |
---|---|
R023XY051NV |
SANDY 8-12 P.Z. |
R024XY066NV |
SODIC DUNES |
Similar sites
R024XY066NV |
SODIC DUNES SAVE4 dominant shrub; less productive site |
---|---|
R023XY051NV |
SANDY 8-12 P.Z. not on sand hills; slopes less than 8 percent; HECO26 codominant grass |
Table 1. Dominant plant species
Tree |
Not specified |
---|---|
Shrub |
(1) Artemisia tridentata ssp. tridentata |
Herbaceous |
(1) Achnatherum hymenoides |
Physiographic features
This site occurs on partially stabilized sand dunes and sand sheets. Slopes range from 2 to 15 percent. Elevations are 4000 to 5900 feet.
Table 2. Representative physiographic features
Landforms |
(1)
Dune
(2) Sand sheet |
---|---|
Elevation | 1,219 – 1,798 m |
Slope | 2 – 15% |
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 8 to 10 inches. Mean annual air temperature is 45 to 50 degrees F. The average growing season is about 90 to 130 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) | 110 days |
---|---|
Freeze-free period (average) | |
Precipitation total (average) | 229 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 windblown, fine and loamy fine sands, typically more than 40 inches in depth. The soil profile is excessively drained and free of salts. Because of rapid soil intake and deep percolation of water, the loss of soil moisture due to evaporation is reduced and runoff is very low. These conditions allow deep rooted plants to grow vigorously under arid climatic conditions. The soils are extremely susceptible to wind erosion and small "blow-out" spots are common, and, collectively, may represent as much as 2 percent of the total surface area for the site. The soil series associated with this site include: Zorravista.
Table 4. Representative soil features
Surface texture |
(1) Fine sand (2) Sand (3) Loamy fine sand |
---|---|
Family particle size |
(1) Sandy |
Drainage class | Excessively drained |
Permeability class | Very rapid |
Soil depth | 183 – 213 cm |
Surface fragment cover <=3" | 0% |
Surface fragment cover >3" | 0% |
Available water capacity (0-101.6cm) |
6.1 – 6.35 cm |
Calcium carbonate equivalent (0-101.6cm) |
0 – 5% |
Electrical conductivity (0-101.6cm) |
0 – 4 mmhos/cm |
Sodium adsorption ratio (0-101.6cm) |
0 – 5 |
Soil reaction (1:1 water) (0-101.6cm) |
7.4 – 9 |
Subsurface fragment volume <=3" (Depth not specified) |
0% |
Subsurface fragment volume >3" (Depth not specified) |
0% |
Ecological dynamics
Where management results in abusive livestock use, Indian ricegrass, basin wildrye, needleandthread and fourwing saltbush will decrease in abundance while unpalatable shrubs will increase. When this sites burns, grazing use should be curtailed until perennial grass species are well established and the site is protected from wind erosion.
Fire Ecology:
Fire return intervals in basin big sagebrush are intermediate between mountain big sagebrush (15 to 25 years) and Wyoming big sagebrush (10 to 70 years). A naturally wide variation in fire frequency in this system is expected. Basin big sagebrush is readily killed when aboveground plant parts are charred by fire. Prolific seed production from nearby unburned plants coupled with high germination rates enables seedlings to establish rapidly following fire. Spiny hopsage is considered to be somewhat fire tolerant and often survives fires that kill sagebrush. Mature spiny hopsage generally sprout after being burned. Spiny hopsage is reported to be least susceptible to fire during summer dormancy. Fire top-kills or kills fourwing saltbush, depending upon ecotype. Fourwing saltbush may sprout after top-kill. Fourwing saltbush probably establishes primarily from seed after fire, with some populations also regenerating vegetatively. Winterfat is either killed or top-killed by fire, depending on fire severity. Severe fire can kill the perennating buds located several inches above the ground surface and thus kills the plant. In addition, severe fire usually destroys seed on the plant. Low-severity fire scorches or only partially consumes the aboveground portions of winterfat and thus does not cause high mortality. Indian ricegrass can be killed by fire, depending on severity and season of burn. Indian ricegrass reestablishes on burned sites through seed dispersed from adjacent unburned areas. 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. Thickspike wheatgrass is quite tolerant of fire. Subsurface growing points and primarily rhizomatous reproduction may explain its ability to increase rapidly (within 2-5 years) following burning. Needleandthread is top-killed by fire. It may be killed if the aboveground stems are completely consumed. Needleandthread is classified as slightly to severely damaged by fire. Needleandthread sprouts from the caudex following fire, if heat has not been sufficient to kill underground parts. Recovery usually takes 2 to 10 years.
State and transition model
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View Interactive Models
Click on state and transition labels to scroll to the respective text
State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 1
Reference State
Community 1.1
Community Phase
The reference plant community is dominated by Indian ricegrass, needleandthread, basin big sagebrush and spiny hopsage. Potential vegetative composition is about 55% grasses, 5% forbs and 40% shrubs. Approximate ground cover (basal and crown) is about 20 to 35 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 | 247 | 432 | 555 |
Shrub/Vine | 179 | 314 | 404 |
Forb | 22 | 39 | 50 |
Total | 448 | 785 | 1009 |
Community 1.2
Community Phase
State 2
Current Potential State
Community 2.1
Community Phase
Community 2.2
Community Phase
Pathway a
Community 2.1 to 2.2
Pathway a
Community 2.2 to 2.1
State 3
Shrub 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
Annual State
Community 4.1
Community Phase
Transition A
State 2 to 3
Transition B
State 2 to 4
Transition A
State 3 to 4
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 | 291–573 | ||||
Indian ricegrass | ACHY | Achnatherum hymenoides | 235–314 | – | ||
basin wildrye | LECI4 | Leymus cinereus | 39–118 | – | ||
needle and thread | HECO26 | Hesperostipa comata | 1–78 | – | ||
thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 16–63 | – | ||
2 | Secondary Perennial Grasses | 39–78 | ||||
squirreltail | ELEL5 | Elymus elymoides | 4–24 | – | ||
beardless wildrye | LETR5 | Leymus triticoides | 4–24 | – | ||
Forb
|
||||||
3 | Perennial | 16–63 | ||||
milkvetch | ASTRA | Astragalus | 4–16 | – | ||
Palmer's penstemon | PEPA8 | Penstemon palmeri | 4–16 | – | ||
scurfpea | PSORA2 | Psoralidium | 4–16 | – | ||
princesplume | STANL | Stanleya | 4–16 | – | ||
4 | Annual | 8–24 | ||||
Shrub/Vine
|
||||||
5 | Primary Shrubs | 149–392 | ||||
basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 78–157 | – | ||
spiny hopsage | GRSP | Grayia spinosa | 39–118 | – | ||
fourwing saltbush | ATCA2 | Atriplex canescens | 16–78 | – | ||
winterfat | KRLA2 | Krascheninnikovia lanata | 16–39 | – | ||
6 | Secondary Shrubs | 16–39 | ||||
shadscale saltbush | ATCO | Atriplex confertifolia | 8–16 | – | ||
Nevada jointfir | EPNE | Ephedra nevadensis | 8–16 | – | ||
rubber rabbitbrush | ERNAN5 | Ericameria nauseosa ssp. nauseosa var. nauseosa | 8–16 | – | ||
greasewood | SAVE4 | Sarcobatus vermiculatus | 8–16 | – | ||
horsebrush | TETRA3 | Tetradymia | 8–16 | – |
Interpretations
Animal community
Livestock Interpretations:
This site is suited for livestock grazing. Grazing management should be keyed to fourwing saltbush, winterfat, and perennial grass production. Indian ricegrass is highly palatable to all classes of livestock in both green and cured condition. It supplies a source of green feed before most other native grasses have produced much new growth. 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. Thickspike wheatgrass is palatable to all classes of livestock and wildlife. It is a preferred feed for cattle, sheep, horses, and elk in spring and is considered a desirable feed for deer and antelope in spring. It is considered a desirable feed for cattle, sheep, and horses in summer, fall, and winter. Thickspike wheatgrass's extensive rhizome system allows established stands to withstand heavy grazing and trampling. Needleandthread provides highly palatable forage, especially in the spring before fruits have developed. Needlegrasses are grazed in the fall only if the fruits are softened by rain. Basin big sagebrush may serve as emergency food during severe winter weather, but it is not usually sought out by livestock. Spiny hopsage provides a palatable and nutritious food source for livestock, particularly during late winter through spring. Domestic sheep browse the succulent new growth of spiny hopsage in late winter and early spring. Fourwing saltbush is one of the most palatable shrubs in the West. Its protein, fat, and carbohydrate levels are comparable to alfalfa. It provides nutritious forage for all classes of livestock. Palatability is rated as good for domestic sheep and domestic goats; fair for cattle; fair to good for horses in winter, poor for horses in other seasons. Winterfat is an important forage plant for livestock, especially during winter when forage is scarce. Abusive grazing practices have reduced or eliminated winterfat on some areas even though it is fairly resistant to browsing. Effects depend on severity and season of grazing.
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:
Basin big sagebrush is the least palatable of all the subspecies of big sagebrush. Basin big sagebrush is browsed by mule deer from fall to early spring, but is not preferred. 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. Spiny hopsage provides a palatable and nutritious food source for big game animals. Spiny hopsage is used as forage to at least some extent by domestic goats, deer, pronghorn, and rabbits. Fourwing saltbush provides valuable habitat and year-round browse for wildlife. Fourwing saltbush also provides browse and shelter for small mammals. Additionally, the browse provides a source of water for black-tailed jackrabbits in arid environments. Granivorous birds consume the fruits. Wild ungulates, rodent and lagomorphs readily consume all aboveground portions of the plant. Palatability is rated good for deer, elk, pronghorn and bighorn sheep. Winterfat is an important forage plant for wildlife, especially during winter when forage is scarce. Winterfat seeds are eaten by rodents and are a staple food for black-tailed jackrabbits. Mule deer and pronghorn antelope browse winterfat. Winterfat is used for cover by rodents. It is potential nesting cover for upland game birds, especially when grasses grow up through its crown. Indian ricegrass is eaten by pronghorn in moderate amounts whenever available. A number of heteromyid rodents inhabiting desert rangelands show preference for seed of Indian ricegrass. Indian ricegrass is an important component of jackrabbit diets in spring and summer. Indian ricegrass seed provides food for many species of birds. Doves, for example, eat large amounts of shattered Indian ricegrass seed lying on the ground. 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. In the spring, thickspike wheatgrass is a preferred feed for elk and is considered desirable feed for deer and antelope. It is desirable feed for elk during summer, fall, and winter. Thickspike wheatgrass is also a component of black-tailed jackrabbit diets. Thickspike wheatgrass provides some cover for small mammals and birds. Needleandthread is moderately important spring forage for mule deer, but use declines considerably as more preferred forages become available.
Hydrological functions
Runoff is very low. Permeability is very rapid.
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
Some Native American peoples used the bark of big sagebrush to make rope and baskets. Some Native American peoples traditionally ground parched seeds of spiny hopsage to make pinole flour. Fourwing saltbush is traditionally important to Native Americans. They ground the seeds for flour. The leaves, placed on coals, impart a salty flavor to corn and other roasted food. Top-growth produces a yellow dye. Young leaves and shoots were used to dye wool and other materials. The roots and flowers were ground to soothe insect bites. Indian ricegrass was traditionally eaten by some Native Americans. The Paiutes used the seed as a reserve food source. Basin wildrye was used as bedding for various Native American ceremonies, providing a cool place for dancers to stand.
Other information
Basin big sagebrush shows high potential for range restoration and soil stabilization. Basin big sagebrush grows rapidly and spreads readily from seed. Spiny hopsage has moderate potential for erosion control and low to high potential for long-term revegetation projects. It can improve forage, control wind erosion, and increase soil stability on gentle to moderate slopes. Spiny hopsage is suitable for highway plantings on dry sites in Nevada. Fourwing saltbush is widely used in rangeland reclamation projects, including burned area recovery. It is probably the most widely used shrub for restoration of winter ranges and mined land reclamation. Winterfat adapts well to most site conditions, and its extensive root system stabilizes soil. However, winterfat is intolerant of flooding, excess water, and acidic soils. 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. Thickspike is a good revegetation species because it forms tight sod under dry rangeland conditions, has good seedling strength, and performs well in low fertility or eroded sites. It does not compete well with aggressive introduced grasses during the establishment period, but are very compatible with slower developing natives, bluebunch wheatgrass (Pseudoroegneria spicata), western wheatgrass (Pascopyrum smithii), and needlegrass (Achnatherum spp.) species. It’s drought tolerance combined with rhizomes, fibrous root systems, and good seedling vigor make these species ideal for reclamation in areas receiving 8 to 20 inches annual precipitation. Thickspike wheatgrass can be used for hay production and will make nutritious feed, but is more suited to pasture use. Needleandthread is useful for stabilizing eroded or degraded sites.
Supporting information
Type locality
Location 1: Washoe County, NV | |
---|---|
Township/Range/Section | T36N R17E S19 |
Latitude | 40° 58′ 18″ |
Longitude | 120° 4′ 45″ |
General legal description | NE 1/4 SE 1/4, West side of Nevada Highway 447, Duck Flat area, Washoe 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
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) | P.Novak-Echenique |
---|---|
Contact for lead author | State Rangeland Management Specialist |
Date | 08/02/2011 |
Approved by | Kendra Moseley |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
None. -
Presence of water flow patterns:
Water flow patterns none. -
Number and height of erosional pedestals or terracettes:
Pedestals are few with occurrence due to wind scouring. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground 50 to 60%. -
Number of gullies and erosion associated with gullies:
Gullies are none. -
Extent of wind scoured, blowouts and/or depositional areas:
Slight to moderate wind scouring.
-
Amount of litter movement (describe size and distance expected to travel):
Fine litter (foliage from grasses and annual and perennial forbs) expected to move unsheltered distance during heavy wind. Persistent litter (large woody material) will remain in place except during intense summer convection storms. -
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 1 to 3 on the sandy soils textures found on the site. (To be field tested). -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Surface structure is single grained. Soil surface colors are light grey. Organic matter of the surface 2 to 3 inches is typically 1 to 1.5% dropping off quickly below. Organic matter content can be more or less depending on microtopography. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Perennial herbaceous plants (especially deep-rooted bunch grasses[i.e. Indian rice grass]) slow runoff and increase in infiltration. Shrub canopy and associated litter break raindrop impact. -
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. -
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 bunch grasses> tall shrubs (Basin big sagebrush)Sub-dominant:
>>associated shrubs>cool season, perennial, rhizomatous grass>shallow-rooted cool season perennial bunchgrasses> deep-rooted, cool season, perennial forbs=fibrous, shallow-rooted, cool season, annual and perennial forbs.Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Dead branches within individual shrubs common in standing dead shrub canopy material may be as much as 25% of total woody canopy; some of the mature bunch grasses (<25%) have dead centers. -
Average percent litter cover (%) and depth ( in):
Between plant interspaces (10-20%) and depth (0.25 in). -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
For normal or average growing season (February through May) +/- 700 lbs/ac; spring moisture significantly affects total 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:
Increasers include rubber rabbitbrush and horsebrush. Potential invaders include cheat grass, halogeton, Russian thistle and annual mustards. -
Perennial plant reproductive capability:
All functional groups should reproduce in average (or normal) and above-average growing season years.
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