Natural Resources
Conservation Service
Ecological site R035XE503AZ
Mudstone Hills 6-10" p.z. Gypsiferous
Last updated: 5/19/2025
Accessed: 12/06/2025
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.
MLRA notes
Major Land Resource Area (MLRA): 035X–Colorado Plateau
AZ CRA 35.5 – Grand Canyon Corridor
Elevations range from 1600 to 4500 feet and precipitation averages 6 to 10 inches per year. Extreme elevation and aspect changes make this area unique. Vegetation includes Mormon tea, catclaw, white brittlebush, blackbrush, prickly pear, cholla species, big galleta, and blue threeawn. The soil temperature regime ranges from thermic to mesic and the soil moisture regime is typic aridic. This unit occurs within the Colorado Plateau Physiographic Province and is characterized by extreme vertical escarpments and strong aspect differences over short distances. Sedimentary rock classes dominate the Grand Canyon and exposures consist of a thick sequence of relatively undeformed formations.
Table 1. Dominant plant species
| Tree |
Not specified |
|---|---|
| Shrub |
(1) Atriplex confertifolia |
| Herbaceous |
(1) Pleuraphis jamesii |
Physiographic features
This site occurs as hummocky and dissected hills and plains of complez gypsiferous shales, mudstones and siltstones. Soil depths range from shallow with lithic outcrop, to deep pockets of alluvium. Slopes are typically 10-30%, but can range from 2-40%. The site occurs on all aspects.
Table 2. Representative physiographic features
| Landforms |
(1)
Hill
(2) Ridge (3) Fan remnant |
|---|---|
| Flooding frequency | None |
| Ponding frequency | None |
| Elevation | 1,600 – 4,600 ft |
| Slope | 2 – 40% |
| Aspect | Aspect is not a significant factor |
Climatic features
The climate of the land resource unit is arid to semiarid with warm summers and cool winters. The mean annual precipitation ranges from 6 – 10 inches, but it is very erratic, often varying substantially from year to year. The majority of the precipitation falls during the between October through May. This precipitation comes as gentile rain or occasionally snow from frontal storms coming out to the Pacific Ocean. Snow is infrequent and rarely last more than 1-2 days. The remaining precipitation comes from July through September as spotty, unreliable and sometimes violent thunderstorms. The moisture for this precipitation originates in the Gulf of Mexico (and the Pacific Ocean in the fall) and flows into the area on the north end of the Mexican monsoon. Late May through late June is generally a dry period. The mean annual air temperature ranges from 55 to 69 degrees Fahrenheit (F). The frost-free period (air temperature > 32 degrees F) ranges from 180 to 220 days (@ 50 percent probability).
Table 3. Representative climatic features
| Frost-free period (average) | 200 days |
|---|---|
| Freeze-free period (average) | 220 days |
| Precipitation total (average) | 10 in |
Figure 1. Monthly precipitation range
Figure 2. Monthly average minimum and maximum temperature
Influencing water features
Soil features
Soil surface textures are loamy very fine to very fine sandy loam and are gravelly to very gravelly. Soil depth can vary from 4-5- inches; it is typically less than 20 inches to a bedrock (paralithic) contact. The surface is strongly to violently effervescent with a significant amount of gypsum content in the A horizon(s). Geologic formation is Hermit formation, Galleros foundation.
Soil temperature regime is Thermic; moisture regime is typic aridic. Water erosion hazard is high; wind erosion hazard is moderate.
Soil diagnostic horizon is Gypsic horizon. Soil restrictive layer is bedrock (paralithic). Soils are slightly alkaline (7.8-8.8), have strong to violent surface effervescence (10-30), are not sodic and very slightly saline.
Soils mapped on this site include:
SSA-701 Grand Canyon Area MU's 129 Torriorthents, 140 Typic haplogypsids (Hermit formation), 141 Haplogypsids, 146 Typic torriorthents and 148 Typic haplogypsids (Hermit formation) & Typic torriorthents (Hermit formation).
Table 4. Representative soil features
| Parent material |
(1)
Alluvium
–
sandstone and shale
(2) Residuum – siltstone |
|---|---|
| Surface texture |
(1) Gravelly loamy very fine sand (2) Very gravelly very fine sandy loam (3) Sandy loam |
| Family particle size |
(1) Loamy |
| Drainage class | Moderately well drained to well drained |
| Permeability class | Moderate to moderately rapid |
| Soil depth | 4 – 50 in |
| Surface fragment cover <=3" | 5% |
| Surface fragment cover >3" | 5% |
| Electrical conductivity (0-40in) |
2 – 8 mmhos/cm |
| Soil reaction (1:1 water) (0-40in) |
7.8 – 8.8 |
| Subsurface fragment volume <=3" (Depth not specified) |
15% |
| Subsurface fragment volume >3" (Depth not specified) |
5% |
Ecological dynamics
For state and transition model see ecological group DX035X02DESG19, Grand Canyon - Typic Aridic - Gypsic Hills.
This site developed under historic Colorado Plateau conditions and reflects the natural influence of herbivores, climate fluctuations, and occasional fire (rare on this site). This state includes the native plant communities that occurred on the site prior to European immigration and settlement.
State and transition model
More interactive model formats are also available.
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Ecosystem states
State 1 submodel, plant communities
State 1
Historic Climax Plant Community
Community 1.1
Historic Climax Plant Community
This community is characterized by widely scattered shrubs that are tolerant of the soil conditions. Dominant species are shadscale saltbush and wolfberry with a variety of other shrubs and sub-shrubs occasionally represented. Perennial grasses can be found in scattered pockets, often in small rills where run-in moisture is a benefit.
Figure 3. 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 | 105 | – | 130 |
| Forb | 10 | – | 25 |
| Grass/Grasslike | 10 | – | 25 |
| Total | 125 | – | 180 |
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 | 5–10 | |||||
| James' galleta | PLJA | Pleuraphis jamesii | 2–5 | – | ||
| big galleta | PLRI3 | Pleuraphis rigida | 2–5 | – | ||
| 2 | 2–5 | |||||
| black grama | BOER4 | Bouteloua eriopoda | 2–5 | – | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 2–5 | – | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 2–5 | – | ||
| gyp dropseed | SPNE | Sporobolus nealleyi | 2–5 | – | ||
| 3 | 2–5 | |||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 2–5 | – | ||
| desert needlegrass | ACSP12 | Achnatherum speciosum | 2–5 | – | ||
| blue threeawn | ARPUN | Aristida purpurea var. nealleyi | 2–5 | – | ||
| smooth oxeye | HEHE5 | Heliopsis helianthoides | 2–5 | – | ||
| 4 | 0–3 | |||||
| Grass, annual | 2GA | Grass, annual | 0–3 | – | ||
|
Forb
|
||||||
| 5 | 8–15 | |||||
| tawny cryptantha | CRFU | Cryptantha fulvocanescens | 2–8 | – | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 2–8 | – | ||
| globemallow | SPHAE | Sphaeralcea | 2–8 | – | ||
| 6 | 0–5 | |||||
| Forb, perennial | 2FP | Forb, perennial | 0–5 | – | ||
| sand verbena | ABRON | Abronia | 0–5 | – | ||
| slender poreleaf | POGR5 | Porophyllum gracile | 0–5 | – | ||
| brownplume wirelettuce | STPA4 | Stephanomeria pauciflora | 0–5 | – | ||
| Mojave woodyaster | XYTO2 | Xylorhiza tortifolia | 0–5 | – | ||
| 7 | 0–5 | |||||
| Forb, annual | 2FA | Forb, annual | 0–5 | – | ||
| milkvetch | ASTRA | Astragalus | 0–5 | – | ||
| Esteve's pincushion | CHST | Chaenactis stevioides | 0–5 | – | ||
| fleabane | ERIGE2 | Erigeron | 0–5 | – | ||
| desertdandelion | MALAC3 | Malacothrix | 0–5 | – | ||
| blazingstar | MENTZ | Mentzelia | 0–5 | – | ||
| popcornflower | PLAGI | Plagiobothrys | 0–5 | – | ||
|
Shrub/Vine
|
||||||
| 8 | 2–15 | |||||
| Subshrub (<.5m) | 2SUBS | Subshrub (<.5m) | 0–5 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–5 | – | ||
| mountain phlox | PHAU3 | Phlox austromontana | 0–5 | – | ||
| Mojave seablite | SUMO | Suaeda moquinii | 0–5 | – | ||
| pricklyleaf dogweed | THAC | Thymophylla acerosa | 0–5 | – | ||
| turpentinebroom | THMO | Thamnosma montana | 0–5 | – | ||
| American threefold | TRCA8 | Trixis californica | 0–5 | – | ||
| 9 | 45–60 | |||||
| shadscale saltbush | ATCO | Atriplex confertifolia | 30–40 | – | ||
| water jacket | LYAN | Lycium andersonii | 30–40 | – | ||
| Arizona desert-thorn | LYEX | Lycium exsertum | 30–40 | – | ||
| 10 | 25–40 | |||||
| catclaw acacia | ACGR | Acacia greggii | 3–10 | – | ||
| honey mesquite | PRGL2 | Prosopis glandulosa | 3–10 | – | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 3–10 | – | ||
| mormon tea | EPVI | Ephedra viridis | 2–8 | – | ||
| Fremont's dalea | PSFR | Psorothamnus fremontii | 2–8 | – | ||
| button brittlebush | ENFR | Encelia frutescens | 2–8 | – | ||
| 11 | 3–10 | |||||
| Shrub, other | 2S | Shrub, other | 0–3 | – | ||
| burrobush | AMDU2 | Ambrosia dumosa | 0–3 | – | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–3 | – | ||
| shortleaf baccharis | BABR | Baccharis brachyphylla | 0–3 | – | ||
| brickellbush | BRICK | Brickellia | 0–3 | – | ||
| blackbrush | CORA | Coleogyne ramosissima | 0–3 | – | ||
| brittlebush | ENFA | Encelia farinosa | 0–3 | – | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–3 | – | ||
| alkali goldenbush | ISAC2 | Isocoma acradenia | 0–3 | – | ||
| 12 | 5–12 | |||||
| beavertail pricklypear | OPBA2 | Opuntia basilaris | 5–12 | – | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 5–12 | – | ||
Interpretations
Supporting information
Contributors
Larry D. Ellicott
Steve Barker
Approval
Kendra Moseley, 5/19/2025
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 | 05/20/2025 |
| 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:
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