Natural Resources
Conservation Service
Ecological site R030XB208AZ
Gypsum Hills
6-9" p.z.
Last updated: 10/21/2024
Accessed: 04/17/2026
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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.
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Figure 1. Mapped extent
Areas shown in blue indicate the maximum mapped extent of this ecological site. Other ecological sites likely occur within the highlighted areas. It is also possible for this ecological site to occur outside of highlighted areas if detailed soil survey has not been completed or recently updated.
MLRA notes
Major Land Resource Area (MLRA): 030X–Mojave Basin and Range
This unit occurs within the Basin and Range Province and is characterized by broad basins, valleys, and old lakebeds. Widely spaced mountains trending north to south occur throughout the area. Isolated, short mountain ranges are separated by an aggraded desert plain. The mountains are fault blocks that have been tilted up. Long alluvial fans coalesce with dry lakebeds between some of the ranges.
LRU notes
AZ LRU 30-2 – Middle Mohave Desert
Elevations range from 1500 to 3200 feet and precipitation averages 6 to 9 inches per year. Vegetation includes creosotebush, white bursage, yucca, prickly pear and cholla species, Mormon tea, flattop buckwheat, ratany, winterfat, bush muhly, threeawns, and big galleta. The soil temperature regime is thermic and the soil moisture regime is typic aridic.Ecological site concept
This ecological site is located on steeply sloping uplands (slopes 15%-65%). Soils very shallow to shallow gypsiferous loam overlying stratified (alternating hard and soft) gypsite.
Associated sites
R030XB205AZ Sandy Loam Upland 6-10" p.z. Limy Subsurface, Gravelly
R030XB210AZ Limestone Hills 6-9" p.z.
R030XB214AZ Limy Upland 6-9" p.z.
R030XB222AZ Gypsum Hills 6-9" p.z. Alkaline
Table 1. Dominant plant species
Tree Not specified
Shrub (1) Ephedra nevadensis
(2) Hymenoclea salsolaHerbaceous Not specified
Physiographic features
This ecological site occurs in an upland position as rounded, eroded hills and escarpments. The soil is very shallow to shallow to gypsiferous layers. Slopes range from 6 to 70 percent.
Table 2. Representative physiographic features
Landforms (1) Escarpment
(2) Hill
Flooding frequency None Ponding frequency None Elevation 1600 – 3400 ft Slope 6 – 70 % Aspect Aspect is not a significant factor Climatic features
The climate is arid and warm. Annual precipitation ranges from 6 to 9 inches. About 65 percent of the rainfall comes from October through May as gentle rain from Pacific storms which may last for a couple of days. The rest of the rainfall comes during the summer monsoon season from July through September as spotty, brief, intense thunderstorms. Snow rarely falls, and only remains on the ground a few hours at most. Annual air temperature ranges from 59 to 70 degrees F. The average frost-free period ranges from 156 to 259 days.
Table 3 Representative climatic features
Frost-free period (average) 260 days Freeze-free period (average) 290 days Precipitation total (average) 10 in BarLineFigure 2. Monthly precipitation range
BarLineFigure 3. Monthly average minimum and maximum temperature
">Influencing water features
Soil features
The soil of this ecological site is very shallow to shallow to gypsiferous layers. The surface texture ranges from fine sandy loam to loam. The subsurface texture is loam. The soil contains high amounts of gypsum. The available water holding capacity is very low. The hazard of erosion by water is very severe and by wind is slight.
A typical soil profile is a follows:
0 to 2 inches - gypsiferous fine sandy loam
2 to 12 inches - gypsiferous loam
12 to 16 inches - alternate layers of soft and hard gypsite
Soil map units correlated to this ecological site include 623030 and 623034, Gypill soil, Shivwits Area SSA.Table 4. Representative soil features
Surface texture (1) Fine sandy loam
(2) Loam
Family particle size (1) Loamy
Drainage class Well drained Permeability class Moderate Soil depth 4 – 15 in Surface fragment cover <=3" Not specified Surface fragment cover >3" Not specified Available water capacity
(0-40in)1.3 – 1.9 in Calcium carbonate equivalent
(0-40in)5 – 35 % Electrical conductivity
(0-40in)0 – 4 mmhos/cm Soil reaction (1:1 water)
(0-40in)7.4 – 8.4 Subsurface fragment volume <=3"
(Depth not specified)Not specified Subsurface fragment volume >3"
(Depth not specified)Not specified Ecological dynamics
Gypsum Hills, 6"-9" p.z., is a sparse shrubland. Perennial grasses and forbs are generally absent. Annual forbs and grasses may encountered following rainfall. Natural disturbances are rare. After introduction of non-native annuals (forbs and/or grasses), the shift in total productivity is shift increased seasonal herbaceous production following periods of rain. Dominant shrubs are Nevada Mormon tea, white bursage, and Fremont dalea. Other assorted half-shrubs are very widely scattered.
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 textEcosystem states
State 1 submodel, plant communities
State 2 submodel, plant communities
State 1
Historic Climax Plant CommunityCommunity 1.1
Historic Climax Plant CommunityThe dominant aspect of this site is desert shrub. The domninant shrubs are Nevada Mormon tea, white burrobrush and Fremont dalea.
With severe disturbance plants that will increase or invade are exotic annuals.
The site's total annual production by weight (air-dried) is comprised of: grasses and grasslike plants - 0 to 2 percent, forbs 1 to 8 percent, and shrubs 90 to 100 percent.Figure 4. 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 24 118 225 Forb 1 6 16 Grass/Grasslike 0 1 4 Total 25 125 245 Table 6. Ground cover
Tree foliar cover 0% Shrub/vine/liana foliar cover 0-0% Grass/grasslike foliar cover 0-0% Forb foliar cover 0-0% Non-vascular plants 0% Biological crusts 0% Litter 0% Surface fragments >0.25" and <=3" 0% Surface fragments >3" 0% Bedrock 0% Water 0% Bare ground 0% Table 7. Canopy structure (% cover)
Height Above Ground (ft) Tree Shrub/Vine Grass/
GrasslikeForb <0.5 – – 0-1% 0-1% >0.5 <= 1 – – – – >1 <= 2 – – – – >2 <= 4.5 – 4-6% – – >4.5 <= 13 – – – – >13 <= 40 – – – – >40 <= 80 – – – – >80 <= 120 – – – – >120 – – – – Figure 5. Plant community growth curve (percent production by month). AZ3022 , 30.2 6-9" p.z. upland sites. Growth begins in the late winter, most growth occurs in the spring..
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec J F M A M J J A S O N D 0 2 19 33 18 7 7 11 3 0 0 0 Figure 6. Plant community growth curve (percent production by month). AZ3074 , 30.23, 6-9 p.z., Nevada Mormon Tea. Growth primarily in spring and early summer months..
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec J F M A M J J A S O N D 0 0 15 25 20 15 15 10 0 0 0 0 State 2
Historic Native Plant Community plus Introduced AnnualsCommunity 2.1
Non-native AnnualsThis plant community resembles the historic native plant community, but exotic annuals have been introduced. Non-native species include red brome, Mediterranean grass (Schismus spp.), and filaree. The flourish of non-native annuals that occurs following rainfalls may preclude native annuals.
Transition T1A
State 1 to 2Introduction of non-native annual forb and grass seed.
Restoration pathway R2A
State 2 to 1None known.
Additional community tables
Table 8. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 0–1 gyp dropseed SPNE Sporobolus nealleyi 0–1 – 2 0–1 Grass, perennial 2GP Grass, perennial 0–1 – Forb3 0–6 Forb, perennial 2FP Forb, perennial 0–6 – 4 0–4 Forb, annual 2FA Forb, annual 0–4 – Shrub/Vine5 38–50 Nevada jointfir EPNE Ephedra nevadensis 38–50 – 6 19–31 burrobrush HYSA Hymenoclea salsola 19–31 – 7 12–19 Fremont's dalea PSFR Psorothamnus fremontii 12–19 – 8 6–19 water jacket LYAN Lycium andersonii 6–19 – 9 1–2 fourwing saltbush ATCA2 Atriplex canescens 1–2 – 10 0–19 banana yucca YUBA Yucca baccata 0–19 – 11 0–6 creosote bush LATR2 Larrea tridentata 0–6 – 12 0–6 winterfat KRLA2 Krascheninnikovia lanata 0–6 – 13 1–5 Shrub (>.5m) 2SHRUB Shrub (>.5m) 1–5 – Table 9. Community 2.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Interpretations
Supporting information
Contributors
Larry D. Ellicott
Stephen CassadyApproval
Kendra Moseley, 10/21/2024
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 04/17/2026 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
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Presence of water flow patterns:
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Number and height of erosional pedestals or terracettes:
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Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
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Number of gullies and erosion associated with gullies:
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Extent of wind scoured, blowouts and/or depositional areas:
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Amount of litter movement (describe size and distance expected to travel):
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Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
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Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
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Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
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Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
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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:
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Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
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Average percent litter cover (%) and depth ( in):
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Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
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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:
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Perennial plant reproductive capability:
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