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Ecological site R035XC334AZ

Sandy Loam Upland 10-14" p.z. Calcareous

Accessed: 12/22/2024

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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.

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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): 035X–Colorado Plateau

AZ CRA 35.3 – Colorado Plateau Sagebrush – Grasslands

Elevations range from 4500 to 6000 feet and precipitation averages 10 to 14 inches. Vegetation includes Wyoming big sagebrush, Utah juniper, Colorado pinyon - cliffrose, Mormon tea, fourwing saltbush, blackbrush Indian ricegrass, needle and thread, western wheatgrass Galleta, black grama, blue grama, and sand dropseed. The soil temperature regime is mesic and the soil moisture regime is ustic aridic. This unit occurs within the Colorado Plateau Physiographic Province and is characterized by a sequence of flat to gently dipping sedimentary rocks eroded into plateaus, valleys and deep canyons. Sedimentary rock classes dominate the plateau with volcanic fields occurring for the most part near its margin.

Table 1. Dominant plant species

Tree	Not specified
Shrub	(1) Ephedra nevadensis (2) Atriplex canescens
Herbaceous	(1) Hesperostipa comata (2) Bouteloua gracilis

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Physiographic features

This site occurs on undulating plateaus, fan terraces, and alluvial fans on toe slopes, foot slopes, side slopes and depressions.

Table 2. Representative physiographic features

Landforms	(1) Plateau (2) Terrace (3) Fan
Flooding frequency	None to rare
Ponding duration	Very brief (4 to 48 hours) to brief (2 to 7 days)
Ponding frequency	None to rare
Elevation	4,800 – 6,300 ft
Slope	1 – 15%
Aspect	Aspect is not a significant factor

Climatic features

Winter summer moisture ratios range from 70:30 to 60:40. Late spring is usually the driest period, and early fall moisture can be sporadic. Summer rains fall from June through September; moisture originates in the Gulf of Mexico and creates convective, usually brief, intense thunderstorms. Cool season moisture from October through May tends to be frontal; it originates in the Pacific and the Gulf of California and falls in widespread storms with longer duration and lower intensity. Precipitation generally comes as snow from December through February. Accumulations above 12 inches are not common but can occur. Snow usually lasts for 3-4 days, but can persist much longer. Summer daytime temperatures are commonly 95 - 100 F and on occasion exceed 105 F. Winter air temperatures can regularly go below 10 F and have been recorded below - 20 F.

Table 3. Representative climatic features

Frost-free period (average)	168 days
Freeze-free period (average)	193 days
Precipitation total (average)	14 in

Bar

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Figure 2. Monthly precipitation range

Bar

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Figure 3. Monthly average minimum and maximum temperature

Soil features

Soils on this site are deep to very deep. Surface textures are fine sandy loam and sandy loam. Subsurface textures are loamy fine sand, fine sandy loam, loam, and sandy clay loam. They are derived from mixed alluvium and alluvium from shale and sandstone. Soil moisture regime is ustic aridic and soil temperature regime is mesic. They are calcareous at the surface.

Typical taxonomic units on this site include:

SSA 623 Shivwits Area MU 11 Anasazi family;
SSA 625 Mohave County NE part MU's 4 Begay, 32 Progresso, 43 & 45 Penestaja, 44 Palma, and 50 Radnick;
SSA 701 Grand Canyon Area MU 157 Ustic torriorthents.

Table 4. Representative soil features

Parent material	(1) Alluvium – sandstone and shale
Surface texture	(1) Fine sandy loam (2) Sandy loam
Family particle size	(1) Loamy
Drainage class	Moderately well drained to well drained
Permeability class	Moderate to moderately rapid
Soil depth	40 – 60 in
Surface fragment cover <=3"	15%
Surface fragment cover >3"	10%
Available water capacity (0-40in)	2.5 – 10 in
Calcium carbonate equivalent (0-40in)	5 – 30%
Electrical conductivity (0-40in)	2 mmhos/cm
Sodium adsorption ratio (0-40in)	5
Soil reaction (1:1 water) (0-40in)	8.2 – 8.6
Subsurface fragment volume <=3" (Depth not specified)	10%

Ecological dynamics

The plant communities found on an ecological site are naturally variable. Composition and production will vary with yearly conditions, location, aspect, and the natural variability of the soils. The historical climax plant community represents the natural potential plant communities found on relict or relatively undisturbed sites. Other plant communities described here represent plant communities that are known to occur when the site is disturbed by factors such as grazing, fire, or drought.

Production data provided in this site description is standardized to air-dry weight at the end of the summer growing season. The plant communities described in this site description are based on near normal rainfall years.

NRCS uses a Similarity Index to compare existing plant communities to the plant communities described here. Similarity Index is determined by comparing the production and composition of a plant community to the production and composition of a plant community described in this site description. To determine Similarity Index, compare the production (air-dry weight) of each species to that shown in the plant community description. For each species, count no more than the maximum amount shown for the species, and for each group, count no more than the maximum shown for the group. Divide the resulting total by the total normal year production shown in the plant community description. If rainfall has been significantly above or below normal, use the total production shown for above or below normal years. If field data is not collected at the end of the summer growing season, then the field data must be corrected to the end of the year production before comparing it to the site description. The growth curve can be used as a guide for estimating production at the end of the summer growing season.

The State and Transition model shows the most common occurring plant communities likely to be encountered on this ecological site. This model may not show every possible plant community, but only those that are most prevalent and observed through field inventory. As more data is collected and research is available, these plant communities may be revised, removed, and even added to reflect the ecological dynamics of this site.

State and transition model

Custom diagram

Standard diagram

Figure 4. State and Transition Model - R035XC334AZ

More interactive model formats are also available. View Interactive Models

More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective text

Ecosystem states

1. Reference

State 1 submodel, plant communities

1.1. Grassland with Shrubs

State 1
Reference

Community 1.1
Grassland with Shrubs

Figure 5. Sandy Loam Upland 10-14" p.z. Calcareous

This site has a plant community made up primarily of mid and short grasses with a relatively small percentage of forbs and shrubs. In the original plant community there is a predominance of warm season grasses with shrubs, half shrubs, and cool season grasses. The dominant aspect is desert grassland with scattered shrubs. Plant species most likely to invade or increase on this site when it deteriorates are broom snakeweed, stickyleaf low rabbitbrush, annuals, and juniper. Continuous grazing during the winter and spring periods will decrease the cool season grasses, which are replaced by warm season, lower forage value grasses and shrubs.

Figure 6. 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)
Grass/Grasslike	360	460	555
Shrub/Vine	80	100	120
Forb	30	40	50
Tree	2	3	4
Total	472	603	729

Table 6. Ground cover

Tree foliar cover	0%
Shrub/vine/liana foliar cover	1-5%
Grass/grasslike foliar cover	10-25%
Forb foliar cover	0-1%
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. Soil surface cover

Tree basal cover	0-1%
Shrub/vine/liana basal cover	1-3%
Grass/grasslike basal cover	2-8%
Forb basal cover	1-3%
Non-vascular plants	0%
Biological crusts	0-15%
Litter	15-25%
Surface fragments >0.25" and <=3"	0-5%
Surface fragments >3"	0-5%
Bedrock	0%
Water	0%
Bare ground	40-60%

Table 8. Canopy structure (% cover)

Height Above Ground (ft)	Tree	Shrub/Vine	Grass/ Grasslike	Forb
<0.5	–	–	–	0-1%
>0.5 <= 1	–	1-2%	5-10%	0-1%
>1 <= 2	–	1-3%	5-25%	–
>2 <= 4.5	0-1%	0-1%	–	–
>4.5 <= 13	0-1%	–	–	–
>13 <= 40	–	–	–	–
>40 <= 80	–	–	–	–
>80 <= 120	–	–	–	–
>120	–	–	–	–

Figure 7. Plant community growth curve (percent production by month). AZ3501, 35.3 10-14" p.z. needle and thread. Growth starts in spring and extends into summer, plants may be green in the fall..

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	10	20	30	10	5	5	10	10	0	0

Figure 8. Plant community growth curve (percent production by month). AZ3503, 35.3 10-14" p.z. galleta. Growth begins in spring, most growth occurs during summer and early fall rainy season. Plants will green up again in the fall..

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	0	0	5	20	15	20	30	10	0	0

Figure 9. Plant community growth curve (percent production by month). AZ3504, 35.3 10-14" p.z. bottlebrush squirreltail. Growth occurs in late winter, spring, and fall. Plants often remain green through the winter..

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	5	15	35	25	10	0	0	5	5	0	0

Figure 10. Plant community growth curve (percent production by month). AZ5104, 35.3 10-14" p.z. sand dropseed. Growth begins in spring and extends into the fall..

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	0	5	10	5	30	35	15	0	0	0

Figure 11. Plant community growth curve (percent production by month). AZ3505, 35.3 10-14" p.z. Indian ricegrass. Growth begins in spring, with semi-dormancy occurring during July through August. Plants will green up again in the fall..

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	10	20	25	20	5	5	10	5	0	0

Figure 12. Plant community growth curve (percent production by month). AZ3531, 35.3 10-14" p.z. all sites. Growth begins in the spring and continues through the summer..

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	1	3	17	18	10	19	20	10	1	1	0

Figure 13. Plant community growth curve (percent production by month). AZ3533, Nevada mormon tea. Grows mainly in spring and early summer..

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	5	25	25	20	15	10	0	0	0	0

Figure 14. Plant community growth curve (percent production by month). AZ3536, Black Grama. Grows mainly on summer precipitation..

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	0	0	5	5	30	50	10	0	0	0

Figure 15. Plant community growth curve (percent production by month). AZ3563, 35.3 10-14" p.z. fourwing saltbush. Growth occurs in late spring through summer..

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	0	0	10	25	35	25	5	0	0	0

Figure 16. Plant community growth curve (percent production by month). AZ3567, 35.3 10-14" p.z. blue grama. Growth occurs mostly during the summer rainy season..

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	0	0	5	5	30	55	5	0	0	0

Additional community tables

Table 9. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Tree
1	Tree Group			0–6
	Utah juniper	JUOS	Juniperus osteosperma	0–6	–
Shrub/Vine
2	Dominant Shrub Group			35–125
	Nevada jointfir	EPNE	Ephedra nevadensis	30–60	–
	yellow rabbitbrush	CHVI8	Chrysothamnus viscidiflorus	0–30	–
	fourwing saltbush	ATCA2	Atriplex canescens	6–24	–
	broom snakeweed	GUSA2	Gutierrezia sarothrae	0–18	–
6	Other shrubs			5–50
	Shrub (>.5m)	2SHRUB	Shrub (>.5m)	6–24	–
	Wyoming big sagebrush	ARTRW8	Artemisia tridentata ssp. wyomingensis	0–6	–
	Wiggins' cholla	CYEC3	Cylindropuntia echinocarpa	0–6	–
	mormon tea	EPVI	Ephedra viridis	0–6	–
	winterfat	KRLA2	Krascheninnikovia lanata	0–6	–
	pale desert-thorn	LYPA	Lycium pallidum	0–6	–
	plains pricklypear	OPPO	Opuntia polyacantha	0–6	–
	whitestem paperflower	PSCO2	Psilostrophe cooperi	0–6	–
	narrowleaf yucca	YUAN2	Yucca angustissima	0–6	–
Grass/Grasslike
3	Dominant Perennial Grasses			230–450
	blue grama	BOGR2	Bouteloua gracilis	90–151	–
	James' galleta	PLJA	Pleuraphis jamesii	60–121	–
	squirreltail	ELELE	Elymus elymoides ssp. elymoides	60–90	–
	threeawn	ARIST	Aristida	6–30	–
	black grama	BOER4	Bouteloua eriopoda	6–30	–
	sand dropseed	SPCR	Sporobolus cryptandrus	6–30	–
1	Co-Dominant Perennial Grasses			120–240
	Indian ricegrass	ACHY	Achnatherum hymenoides	60–121	–
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	60–121	–
2	Other perennial grasses			0–15
	Grass, perennial	2GP	Grass, perennial	0–6	–
	mat muhly	MURI	Muhlenbergia richardsonis	0–6	–
	slim tridens	TRMU	Tridens muticus	0–6	–
3	Other annual grasses			0–15
	Grass, annual	2GA	Grass, annual	0–6	–
	cheatgrass	BRTE	Bromus tectorum	0–6	–
	sixweeks fescue	VUOC	Vulpia octoflora	0–6	–
Forb
4	Dominant Forb			5–15
	globemallow	SPHAE	Sphaeralcea	6–18	–
4	Other perennial forbs			5–15
	Forb, perennial	2FP	Forb, perennial	6–18	–
	ragweed	AMBRO	Ambrosia	0–6	–
	mariposa lily	CALOC	Calochortus	0–6	–
	larkspur	DELPH	Delphinium	0–6	–
	phlox	PHLOX	Phlox	0–6	–
	ragwort	SENEC	Senecio	0–6	–
5	Other annual forbs			10–20
	Forb, annual	2FA	Forb, annual	12–18	–
	aster	ASTER	Aster	6–12	–
	milkvetch	ASTRA	Astragalus	0–6	–
	tansymustard	DESCU	Descurainia	0–6	–
	buckwheat	ERIOG	Eriogonum	0–6	–
	sunflower	HELIA3	Helianthus	0–6	–
	plantain	PLANT	Plantago	0–6	–
	prickly Russian thistle	SATR12	Salsola tragus	0–6	–

Interpretations

Animal community

Site is favorable for grazing throughout most of the year except when snow cover restricts availability of forage. With continuous grazing use during winter and spring, the cool season mid grasses are replaced by stickyleaf low rabbitbrush, snakeweed and lower value forbs and grasses. Planned grazing systems adapt well to use on this site.

The potential plant community produced by this site provides food for those species of wildlife that utilize grass as a major portion of their diet. When vegetative retrogression occurs, unpalatable shrubby species increase and some wildlife species may be benefit.

Wildlife that frequents the area: Pronghorn antelope, Black-tailed jackrabbit, coyote, badger, Antelope squirrel, Kangaroo rat, deer mouse, Red tail hawk, Raven, meadowlark, gopher snake, Western rattlesnake, Longnose leopard lizzard, Short-horned lizzard, western whiptail, and Black-collared lizzard.

Recreational uses

Site is typically fans and terraces. It produces high desert grasslands which can be very picturesque.

Winters are cold, however, relatively mild spring, fall and summer months are attractive to recreationists.

Activities include hunting, cross-country riding, photography, hiking, rock collecting, and wildlife observation.

Supporting information

Type locality

Location 1: Mohave County, AZ
Township/Range/Section	T36n R10w S31
General legal description	Poverty Knoll 7 1/2 Min. Quad; Approximately 7 miles Northwest of Mount Trumbull; Section 31, T36N, R10W; Mohave County, AZ.

Other references

Updates and revisions for this ESD were conducted as part of a 2007-2012 Interagency Technical Assistance Agreement between the Bureau of Indian Affairs–Navajo Region and the NRCS-Arizona.

Contributors

Larry D. Ellicott
Steve Barker

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)	Kenneth Gishi
Contact for lead author	State Rangeland Management Specialist, NRCS-Arizona State Office, Phoenix, AZ
Date	08/06/2012
Approved by
Approval date
Composition (Indicators 10 and 12) based on	Annual Production

Indicators

Number and extent of rills:
None. Due to the low to medium runoff, well to somewhat excessively drained and moderate to rapid permeability, rills would not be expected on this site.
Presence of water flow patterns:
None on level slopes due to the low to medium runoff, well to somewhat excessively drained and moderate to rapid permeability, water patterns would not be expected on this site. On steeper slopes, a few water flow patterns may be present, especially following large storm events or where adjacent to rock outcrops.
Number and height of erosional pedestals or terracettes:
There may be a few occasional pedestals and terracettes, especially on steeper slopes and/or during a drought, due to the high wind erosion hazards of the soils
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground (soil surface cover) ranges from 40-60%. This site has the potential to produce a moderate amount of plant cover and litter due to an average availability of water capacity of 6-10 inches. Drought may cause an increase in bare ground.
Number of gullies and erosion associated with gullies:
None. Any gullies present are stabilized with grasses and shrubs and should not be actively eroding.
Extent of wind scoured, blowouts and/or depositional areas:
Some wind scoured areas, blowouts and/or depositional areas may occur, especially during droughts due to high wind erosion hazard of the soils. There may be some slight deposition around long lived shrubs.
Amount of litter movement (describe size and distance expected to travel):
The majority of herbaceous and fine woody litter will be transported by wind and some by water in flow pathways. Coarse woody litter will remain under shrub and tree canopies.
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil surface textures ranging from loamy fine sand to loam. When well vegetated, these soils have a moderate to high resistance to water erosion, but only a moderate resistance to wind erosion. Expected stability ratings of 4-5 under canopies and 2-3 in the interspaces.
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Most soils have a fine granular structure. The typical thickness of the A-horizon is 3-8 inches. Typical surface color is yellowish red (5YR 5/6).
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
This site is characterized by a dominance of grasses with scattered shrubs, with lesser amounts of forbs and trees. Trees are often widely scattered sparsely across the site. Canopy cover ranges from 15-30% (grasses >> shrubs > forbs> trees and cacti). Basal cover ranges from 5-12% for vascular plants and 0-15% for biological crust. Both canopy and basal cover values decrease during a prolonged drought. This type of plant community is moderately effective at capturing and storing precipitation.
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
None. These soils are not easily compacted. Some soils may have a massive structure and should not be confused with a compacted layer.
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:
Cool season grasses (needle and thread, Indian ricegrass, squirreltail) > Warm season grasses (blue grama, black grama, galleta, sand dropseed) >

Sub-dominant:
Shrubs (Mormon tea, fourwing saltbush, rabbitbrush, snakeweed > Forbs > Trees

Other:
Cacti & Yucca

Additional:
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
All plant functional groups are adapted to survival in all but the most severe droughts. Severe winter droughts affect shrubs and trees the most. Severe summer droughts affect grasses the most.
Average percent litter cover (%) and depth ( in):
Litter depth ranges from 1 leaf thickness to 2 inches. Of the total litter amount, it would be expected that up to 90% would be herbaceous litter and 10-30 percent would be woody litter. There may be a slight increase of litter following a drought and decrease in later years.
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
The expected total annual production is 550 – 650 lbs/ac in a normal precipitation year.
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:
Broom snakeweed, Greene's rabbitbrush, prickly pear, and juniper are all natives that have the potential to increase and co-dominate after disturbance. Cheatgrass and Russian thistle is an exotic annual that is becoming endemic to the site regardless of management or disturbance.
Perennial plant reproductive capability:
All plants native to the site are adapted to the climate and are capable of producing seeds, stolons, and/or rhizomes except during the most severe drought.

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