
Natural Resources
Conservation Service
Ecological site R030XA044NV
LOAMY HILL 5-7 P.Z.
Last updated: 2/18/2025
Accessed: 03/15/2025
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
This site occurs on hills, mesas, and fan remnants on all aspects. Slopes range from 2 to 50 percent. Elevations are 3000 to 6400 feet. The soils associated with this site are very shallow to very deep and well to excessively well drained. These soils have formed in residuum from volcanic parent material. The soil profile is modified with 50 to 75 percent rock fragments and more then half of these fragments are cobbles and stones.
Please refer to group concept R030XA045CA to view the provisional STM.
Similar sites
R030XA068NV |
CALCAREOUS HILL 5-7 P.Z. LATR2 codominant shrub, otherwise a very similar site and may be able to correlate |
---|---|
R030XA056NV |
LOAMY HILL 3-5 P.Z. LYAN & Ephedra minor spp. |
R030XA059NV |
GRAVELLY HILL 5-7 P.Z. ATCO-LATR2 codominant; LYAN & MESP2 minor shrubs, if present |
R030XA066NV |
CALCAREOUS LOAM 5-7 P.Z. AMDU2-ATCO codominant |
R030XA061NV |
LOAMY 5-7 P.Z. Not on hills; slopes typically <15%; greater shrub diversity |
R030XA002NV |
LIMESTONE HILL 5-7 P.Z. Soils from limestone PM; LYAN minor spp., if present |
Table 1. Dominant plant species
Tree |
Not specified |
---|---|
Shrub |
(1) Atriplex confertifolia |
Herbaceous |
(1) Achnatherum speciosum |
Physiographic features
This site occurs on hills, mesas, and fan remnants on all aspects. Slopes range from 2 to 50 percent. Elevations are 3000 to 6400 feet.
Table 2. Representative physiographic features
Landforms |
(1)
Hill
(2) Mesa (3) Fan remnant |
---|---|
Elevation | 3,000 – 6,400 ft |
Slope | 2 – 50% |
Aspect | Aspect is not a significant factor |
Climatic features
The climate is hot and arid, with mild winters and very hot summers. Precipitation is greatest in the winter with a lesser secondary peak in summer, typical of the Mojave Desert. Average annual precipitation is 5 to 7 inches. Mean annual air temperature is 56 to 64 degrees F. The average growing season is about 150 to 230 days.
Table 3. Representative climatic features
Frost-free period (average) | 230 days |
---|---|
Freeze-free period (average) | |
Precipitation total (average) | 7 in |
Figure 1. Monthly average minimum and maximum temperature
Influencing water features
There are no influencing water features associated with this site.
Soil features
The soils associated with this site are very shallow to very deep and well to excessively well drained. These soils have formed in residuum from volcanic parent material. The soil profile is modified with 50 to 75 percent rock fragments and more then half of these fragments are cobbles and stones. High amounts of rock fragments occur at the soil surface which occupy plant growing space yet help to reduce evaporation and conserve soil moisture. Coarse fragments on the surface provide a stabilizing affect of surface erosion conditions. Runoff is very high, available water capacity is very low and water intake rates are moderately rapid. The soil series associated with this site includes: Greyeagle, Upspring, and Zalda.
Table 4. Representative soil features
Parent material |
(1)
Residuum
–
volcanic breccia
|
---|---|
Surface texture |
(1) Very gravelly sandy loam (2) Extremely gravelly sandy loam (3) Very cobbly sandy loam |
Family particle size |
(1) Loamy |
Drainage class | Well drained to somewhat excessively drained |
Permeability class | Moderately rapid |
Soil depth | 4 – 84 in |
Surface fragment cover <=3" | 22 – 60% |
Surface fragment cover >3" | 3 – 27% |
Available water capacity (0-40in) |
0.5 – 1.2 in |
Calcium carbonate equivalent (0-40in) |
10% |
Electrical conductivity (0-40in) |
4 mmhos/cm |
Sodium adsorption ratio (0-40in) |
5 |
Soil reaction (1:1 water) (0-40in) |
7.9 – 9 |
Subsurface fragment volume <=3" (Depth not specified) |
12 – 52% |
Subsurface fragment volume >3" (Depth not specified) |
3 – 26% |
Ecological dynamics
Please refer to group concept R030XA045CA to view the provisional STM.
Following surface disturbance or wildfire, introduced annual grasses and forbs readily invade or increase on this site.
Fire Ecology:
The mean fire return interval for shadscale communities range from 35 to 100 years. Shadscale communities are usually unaffected by fire because of low fuel loads, although a year of exceptionally heavy winter rains can generate fuels by producing a heavy stand of annual forbs and grasses. Increased presence of non-native annual grasses, such as cheatgrass, can alter fire regimes by increasing fire frequency under wet to near-normal summer moisture conditions. Torrey’s ephedra has medium fire tolerance and is similar to Nevada ephedra. Nevada ephedra is top-killed by fire. Underground regenerative structures commonly survive when aboveground vegetation is consumed by fire. Nevada ephedra generally sprouts after fire damages aboveground vegetation and may increase in plant cover. Spiny menodora often survives fire because its foliage does not readily burn. Shadscale is fire intolerant and it does not readily recover from fire, except for establishment through seed. Fire generally kills white bursage. However, most white bursage plants burned because their canopies contained numerous small branches in proximity to herbaceous fuels. Desert needlegrass has persistent dead leaf bases, which make it susceptible to burning. Fire removes the accumulation; a rapid, cool fire will not burn deep into the root crown and surviving tufts will resprout. 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. Bottlebrush squirreltail's small size, coarse stems, and sparse leafy material aid in its tolerance of fire. Postfire regeneration occurs from surviving root crowns and from on- and off-site seed sources. Frequency of disturbance greatly influences postfire response of bottlebrush squirreltail. Undisturbed plants within a 6 to 9 year age class generally contain large amounts of dead material, increasing bottlebrush squirreltail's susceptibility to fire.
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
State 1 submodel, plant communities
State 1
Reference State
Community 1.1
Reference Plant Community
The reference plant community is dominated by shadscale, Anderson's wolfberry, Ephedra ssp., and spiny menodora. Potential vegetative composition is about 15% grasses, 5% forbs and 80% shrubs. Approximate ground cover (basal and crown) is 3 to 8 percent.
Figure 2. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
---|---|---|---|
Shrub/Vine | 60 | 120 | 200 |
Grass/Grasslike | 11 | 23 | 38 |
Forb | 4 | 7 | 12 |
Total | 75 | 150 | 250 |
Additional community tables
Table 6. Community 1.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | Primary Perennial Grasses | 7–28 | ||||
desert needlegrass | ACSP12 | Achnatherum speciosum | 3–12 | – | ||
squirreltail | ELEL5 | Elymus elymoides | 2–8 | – | ||
Indian ricegrass | ACHY | Achnatherum hymenoides | 2–8 | – | ||
2 | Secondary Perennial Grasses | 1–8 | ||||
low woollygrass | DAPU7 | Dasyochloa pulchella | 1–5 | – | ||
Forb
|
||||||
3 | Perennial forbs | 1–8 | ||||
4 | Annual forbs | 1–8 | ||||
Shrub/Vine
|
||||||
5 | Primary shrubs | 84–126 | ||||
shadscale saltbush | ATCO | Atriplex confertifolia | 70–88 | – | ||
spiny menodora | MESP2 | Menodora spinescens | 3–15 | – | ||
burrobush | AMDU2 | Ambrosia dumosa | 3–8 | – | ||
Nevada jointfir | EPNE | Ephedra nevadensis | 4–8 | – | ||
Torrey's jointfir | EPTO | Ephedra torreyana | 4–8 | – | ||
6 | Secondary shrubs | 8–23 | ||||
Shockley's goldenhead | ACSH | Acamptopappus shockleyi | 2–5 | – | ||
burrobrush | HYSA | Hymenoclea salsola | 2–5 | – | ||
creosote bush | LATR2 | Larrea tridentata | 2–5 | – | ||
desert pepperweed | LEFR2 | Lepidium fremontii | 2–5 | – | ||
Nevada dalea | PSPO | Psorothamnus polydenius | 2–5 | – |
Interpretations
Animal community
Livestock Interpretations:
This site has limited value for livestock grazing, due to the low forage production, steep slopes and stony surfaces. Desert needlegrass produces considerable basal foliage and is good forage while young. Young desert needlegrass is palatable to all classes of livestock. Mature herbage is moderately grazed by horses and cattle but rarely grazed by sheep. 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. Overall, bottlebrush squirreltail is considered moderately palatable to livestock. Shadscale provides good browse for domestic sheep and goats. Shadscale leaves and seeds are an important component of domestic sheep and cattle winter diets. Shadscale tends to be browse tolerant. Heavy grazing during the winter and/or spring reduces shadscale. Die-off can also occur during extended periods of high precipitation. Shadscale is tolerant of early spring light-intensity browsing. Torrey’s ephedra is important winter forage for cattle and sheep. Torrey’s ephedra is moderately palatable to all domestic livestock especially as winter browse. Nevada ephedra is important winter range browse for domestic cattle, sheep and goats. Nevada ephedra is usually grazed heavily and seems to be perfectly safe for grazing livestock since it induces neither toxicity in ewes or cows, nor congenital deformities in lambs. Cattle will graze the stems of spiny menodora in the spring before the stems become woody and spiny. Spiny menodora has lower palatability than the other shrubs but is consumed during early spring before spines mature. White bursage is of intermediate forage value. It is fair to good forage for horses and fair to poor for cattle and sheep. However, because there is often little other forage where white bursage grows, it is often highly valuable to browsing animals and is sensitive to browsing.
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:
Shadscale is a valuable browse species providing a source of palatable, nutritious forage for a wide variety of wildlife. The fruits and leaves are a food source for deer, desert bighorn sheep and pronghorn antelope. Torrey’s ephedra is an important browse species for big game. Torrey’s ephedra is moderately palatable to many big game species, especially as winter browse. Mule deer, bighorn sheep, and pronghorn browse Nevada ephedra, especially in spring and late summer when new growth is available. Mountain quail eat Ephedra seeds. Elk will graze the stems of spiny menodora in the spring before the stems become woody and spiny. White bursage is an important browse species for wildlife. Desert bighorn sheep and feral horses and burros will graze desert needlegrass. Indian ricegrass is eaten by pronghorn in moderate amounts whenever available. In Nevada it is consumed by desert bighorns. 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. In Nevada, Indian ricegrass may even dominate jackrabbit diets during the spring through early summer months. 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. Bottlebrush squirreltail is a dietary component of several wildlife species. Townsend's ground squirrels, Nuttall's cottontails, and black-tailed jackrabbits all feed upon bottlebrush squirreltail.
Hydrological functions
Runoff is very high. Permeability is moderately rapid.
Other products
Indian ricegrass was traditionally eaten by some Native Americans. The Paiutes used seed as a reserve food source. Seeds of shadscale were used by Native Americans for bread and mush. Some Native American tribes steeped the twigs of Nevada ephedra and drank the tea as a general beverage. White bursage is a host for sandfood, a parasitic plant. Sandfood was a valuable food supply for Native Americans.
Other information
Desert needlegrass may be used for groundcover in areas of light disturbance, but it is susceptible to excessive trampling. White bursage may be used to revegetate disturbed sites in southwestern deserts.
Supporting information
Type locality
Location 1: Nye County, NV | |
---|---|
Township/Range/Section | T9S R46E S10 |
General legal description | Low-lying hills on east side of Sarcobatus Valley, Nye County, Nevada. This site also occurs in southern Nye County. |
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
HA
Approval
Kendra Moseley, 2/18/2025
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 | 02/18/2025 |
Approved by | Kendra Moseley |
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
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.