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Ecological site R030XA109AZ

Limy Upland 3-6" p.z. Deep

Last updated: 10/21/2024
Accessed: 12/03/2024

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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): 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 30-1 – Lower Mohave Desert

Elevations range from 400 to 2500 feet and precipitation averages 3 to 6 inches per year. Vegetation includes creosotebush, white bursage, Mormon tea, and brittlebush. The soil temperature regime is hyperthermic and the soil moisture regime is typic aridic.

Ecological site concept

This ecological site is located on uplands with deep, skeletal soils that are violently effervescent throughout. Gravel-sized fragments armor the soil surface and dominate throughout the soil profile.

Associated sites

R030XA108AZ	Limy Upland 3-6" p.z. Limy Upland, Deep, 3

R030XA108AZ

Limy Upland 3-6" p.z.

Limy Upland, Deep, 3

Table 1. Dominant plant species

Tree	Not specified
Shrub	(1) Larrea tridentata (2) Ambrosia dumosa
Herbaceous	Not specified

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Physiographic features

This site occurs on summits and sideslopes of fan terraces. It occurs on all exposures. Slopes generally range from 1 to 15 percent, but may reach as high as 25 percent. Elevation ranges from 650 feet to 2000 feet above sea level.

Table 2. Representative physiographic features

Landforms	(1) Terrace
Flooding frequency	None
Ponding frequency	None
Elevation	600 – 2,000 ft
Slope	1 – 25%
Aspect	Aspect is not a significant factor

Climatic features

The 30-1AZ Lower Mohave Desert Shrub land resource unit is characterized by a hot, dry climate. The average annual rainfall is 3 to 6 inches, but it can be extremely variable (e.g. from 0 to 11 inches). There can be long periods when little or no precipitation is received. Most of the precipitation for the year could arrive in just a couple of storms. The soil moisture regime is typic aridic and the soil temperature regime is hyperthermic. Winter precipitation from November through April occurs as gentle rains from storms coming out of the Pacific Ocean. Snow is very rare and only falls in the highest mountains. A seasonal drought occurs in May and June. Summer/fall precipitation from July through October comes from spotty, unreliable, and sometimes violent thunderstorms. The moisture originates in the Gulf of Mexico (and the Pacific Ocean in the fall) and flows into the state on the north end of the Mexican monsoon. Strong winds are common, especially during the spring.

Table 3. Representative climatic features

Frost-free period (average)	325 days
Freeze-free period (average)	365 days
Precipitation total (average)	6 in

Bar

Line

Figure 2. Monthly average minimum and maximum temperature

Soil features

These soils are deep to very deep to any plant root restricting layer. They are very coarse textured. The surface layer ranges from extremely gravelly loam to extremely gravelly sandy loam. The subsurface texture ranges from gravelly sandy loam to extremely gravelly loamy sand. The soil is derived from alluvium from volcanics and granitics. A typical profile appears as follows:
0-8 inches - very gravelly sandy loam
8-19 nches - calcareous extremely gravelly coarse sandy loam
19-28 inches - calcareous very gravelly loamy coarse sand
28-44 inches - calcareous extremely gravelly sandy loam
44-60 inches - weakly to strongly silica- and lime-cemented extremely gravelly loamy coarse sand.

Table 4. Representative soil features

Parent material	(1) Alluvium – granite
Surface texture	(1) Extremely gravelly loam (2) Extremely gravelly sandy loam
Family particle size	(1) Sandy
Drainage class	Well drained
Permeability class	Moderately rapid to rapid
Soil depth	44 – 65 in
Surface fragment cover <=3"	40 – 55%
Surface fragment cover >3"	15%
Calcium carbonate equivalent (0-40in)	10 – 30%
Electrical conductivity (0-40in)	4 mmhos/cm
Soil reaction (1:1 water) (0-40in)	7.8 – 8.4
Subsurface fragment volume <=3" (Depth not specified)	20 – 55%
Subsurface fragment volume >3" (Depth not specified)	15%

Ecological dynamics

Limy Upland, 3"-6" p.z., Deep, is a widely dispersed desert shrub community. Natural disturbances are rare. After introduction of non-native annuals (forbs and/or grasses), the shift in total productivity with shift slightly toward seasonal herbaceous production following periods of rain. Livestock and wildlife use are limited on this site due low forage production and dispersed habitat. Dominant shrubs are creosote and white bursage. Assorted half-shrubs are 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 text

State 1
Historic Climax Plant Community

Community 1.1
Historic Climax Plant Community

The dominant aspect of this ecological site is a desert shrub. Creosotebush and white bursage are the major shrubs.

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	68	70	72
Forb	4	11	14
Grass/Grasslike	1	7	10
Total	73	88	96

Table 6. Ground cover

Tree foliar cover	0%
Shrub/vine/liana foliar cover	0-2%
Grass/grasslike foliar cover	0%
Forb foliar cover	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/ Grasslike	Forb
<0.5	–	–	9-2%	0-2%
>0.5 <= 1	–	–	–	–
>1 <= 2	–	5-7%	–	–
>2 <= 4.5	–	–	–	–
>4.5 <= 13	–	–	–	–
>13 <= 40	–	–	–	–
>40 <= 80	–	–	–	–
>80 <= 120	–	–	–	–
>120	–	–	–	–

Figure 4. Plant community growth curve (percent production by month). AZ3011, 30.1 3-6" p.z. all sites. Growth begins in 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	7	30	32	13	7	3	5	2	1	0	0

Figure 5. Plant community growth curve (percent production by month). AZ3082, 30.27 3-6" p.z. creosotebush. Growth occurs mostly in the spring using stored winter moisture. Flowers and sets seed by July..

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	20	40	20	20	0	0	0	0	0	0

Figure 6. Plant community growth curve (percent production by month). AZ3083, 30.27 3-6" p.z. white bursage. Growth begins in early spring. Dormancy occurs during the hot summer months. With sufficient summer/fall precipitation, some plants may break dormancy and produce a flush of growth. Flowers and sets seed by July..

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	20	40	20	15	0	0	0	0	0	0

State 2
Historic Native Plant Community plus Introduced Annuals

Community 2.1
Historic Native Plant Community plus Introduced Annuals

This 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.

Figure 7. Annual production by plant type (representative values) or group (midpoint values)

Table 8. Annual production by plant type

Plant type	Low (lb/acre)	Representative value (lb/acre)	High (lb/acre)
Shrub/Vine	68	70	72
Forb	4	11	14
Grass/Grasslike	1	7	10
Total	73	88	96

Table 9. Ground cover

Tree foliar cover	0%
Shrub/vine/liana foliar cover	0-2%
Grass/grasslike foliar cover	0%
Forb foliar cover	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 10. Canopy structure (% cover)

Height Above Ground (ft)	Tree	Shrub/Vine	Grass/ Grasslike	Forb
<0.5	–	–	0-2%	0-2%
>0.5 <= 1	–	–	–	–
>1 <= 2	–	5-7%	–	–
>2 <= 4.5	–	–	–	–
>4.5 <= 13	–	–	–	–
>13 <= 40	–	–	–	–
>40 <= 80	–	–	–	–
>80 <= 120	–	–	–	–
>120	–	–	–	–

Figure 8. Plant community growth curve (percent production by month). AZ3011, 30.1 3-6" p.z. all sites. Growth begins in 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	7	30	32	13	7	3	5	2	1	0	0

Figure 9. Plant community growth curve (percent production by month). AZ3080, 30.27 3-6" p.z. red brome (exotic). Germinates in October with fall precipitation, most growth occurs in February through April..

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	15	60	20	0	0	0	0	0	5	0	0

Figure 10. Plant community growth curve (percent production by month). AZ3081, 30.27 3-6" p.z. redstem filaree (exotic). Germinates in October with fall precipitation, most growth occurs in February through April..

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	15	60	20	0	0	0	0	0	5	0	0

Figure 11. Plant community growth curve (percent production by month). AZ3082, 30.27 3-6" p.z. creosotebush. Growth occurs mostly in the spring using stored winter moisture. Flowers and sets seed by July..

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	20	40	20	20	0	0	0	0	0	0

Figure 12. Plant community growth curve (percent production by month). AZ3083, 30.27 3-6" p.z. white bursage. Growth begins in early spring. Dormancy occurs during the hot summer months. With sufficient summer/fall precipitation, some plants may break dormancy and produce a flush of growth. Flowers and sets seed by July..

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	20	40	20	15	0	0	0	0	0	0

Transition T1A
State 1 to 2

Wind or mechanical transport of non-native seeds or propagules.

Restoration pathway R2A
State 2 to 1

Non-known.

Additional community tables

Table 11. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Native Perennial Grasses			1–3
	low woollygrass	DAPU7	Dasyochloa pulchella	1–2	–
	big galleta	PLRI3	Pleuraphis rigida	0–1	–
2	Native Annual Grasses			2–6
	Grass, annual	2GA	Grass, annual	2–6	–
Forb
3	Perennial Forbs			1–2
	desert trumpet	ERIN4	Eriogonum inflatum	0–1	–
	desert globemallow	SPAM2	Sphaeralcea ambigua	0–1	–
4	Native Annual Forbs			2–10
	Forb, annual	2FA	Forb, annual	2–10	–
	desert Indianwheat	PLOV	Plantago ovata	0–1	–
Shrub/Vine
5	Native Shrubs			68–72
	creosote bush	LATR2	Larrea tridentata	36–45	–
	burrobush	AMDU2	Ambrosia dumosa	22–27	–
	Nevada jointfir	EPNE	Ephedra nevadensis	1–4	–
	white ratany	KRGR	Krameria grayi	1–4	–
	button brittlebush	ENFR	Encelia frutescens	0–1	–
	rayless goldenhead	ACSP	Acamptopappus sphaerocephalus	0–1	–
6	Native Yuccas			0–3
	Mojave yucca	YUSC2	Yucca schidigera	0–3	–

Table 12. Community 2.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Native Grasses			1–3
	low woollygrass	DAPU7	Dasyochloa pulchella	1–2	–
	big galleta	PLRI3	Pleuraphis rigida	0–1	–
2	Native Annual Grasses			1–2
	Grass, annual	2GA	Grass, annual	1–2	–
3	Introduced Annual Grasses			1–5
	red brome	BRRU2	Bromus rubens	1–5	–
Forb
4	Native Perennial Forbs			0–2
	desert trumpet	ERIN4	Eriogonum inflatum	0–1	–
	desert globemallow	SPAM2	Sphaeralcea ambigua	0–1	–
5	Native Annual Forbs			1–5
	Forb, annual	2FA	Forb, annual	1–4	–
	desert Indianwheat	PLOV	Plantago ovata	0–1	–
6	Introduced Annual Forbs			1–5
	redstem stork's bill	ERCI6	Erodium cicutarium	1–4	–
Shrub/Vine
7	Native Shrubs			68–72
	creosote bush	LATR2	Larrea tridentata	36–45	–
	burrobush	AMDU2	Ambrosia dumosa	22–27	–
	Nevada jointfir	EPNE	Ephedra nevadensis	1–4	–
	white ratany	KRGR	Krameria grayi	1–4	–
	button brittlebush	ENFR	Encelia frutescens	0–1	–
	rayless goldenhead	ACSP	Acamptopappus sphaerocephalus	0–1	–
8	Native Yuccas			0–3
	Mojave yucca	YUSC2	Yucca schidigera	0–3	–

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)	Cody Lunsford and Steve Cassady
Contact for lead author	Steve Cassady, State Rangeland Management Specialist, ph 602.280.8818
Date	04/04/2008
Approved by	Kendra Moseley
Approval date
Composition (Indicators 10 and 12) based on	Annual Production

Indicators

Number and extent of rills:
None. A cover of gravel and rock armor the soil surface against erosion.
Presence of water flow patterns:
Few. This ecological site often occurs along fairly narrow ridge tops. The water flow patterns occur on the side slopes of these ridges as the slope nears 15 percent. Water flow patterns may be observed just above the natural drainages into the washes dissecting the fan terrace the site occurs on. The cover of gravel and rock armors the soil surface against erosion preventing water flow patterns from developing in other locations on the ecological site. No water flow patterns should be observed where the slope is less than 10 percent.
Number and height of erosional pedestals or terracettes:
None. A cover of gravel and rock armors the soil surface against erosion and the creation of pedestals or terracettes.
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground makes up 10 to 20 percent. Rock and gravel cover is 70 to 80 percent. Litter cover is 5 to 15 percent. Basal plant cover is generally less than 5 percent.
Number of gullies and erosion associated with gullies:
Numerous drainages running approximately vertical to the direction of the ridge topography this ecological site generally occurs on may be observed. These are natural and no active erosion is seen associated with them.
Extent of wind scoured, blowouts and/or depositional areas:
None. A cover of gravel and rock armors the soil surface against wind erosion and the resulting scoured, blowout and/or depositional areas.
Amount of litter movement (describe size and distance expected to travel):
Litter is naturally concentrated underneath the scattered shrubs found on this ecological site. The residue of annual forbs and grasses, although naturally scarce, generally stays in place for several months after these plants have senesced due to the soil surface cover of gravel and rock found on this ecological site.
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
No slake test information is available. The soil surface is very resistant to both water and wind erosion due to the cover of rocks and gravels.
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Weak thick platy structure; color is 10YR4/3 moist. The thickness of the A horizon is 2 to 5 inches.
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
This plant community is characterized by widely scattered shrubs with average spacing of 20 to 30 feet. Canopy cover of shrubs is 5 to 15 percent.
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
No compaction layer exists on this ecological site. The soil surface cover of gravel and rock forms a somewhat impenetrable layer, but this is not due to compaction.
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:
shrubs (75-85%)>>

Sub-dominant:
Forbs (5-15%)>> Grasses (1-10%)

Other:

Additional:
During years of above average precipitation the ratio of shrubs to annual plants (dominantly annual forbs) will naturally change with the annually produced biomass produced and resulting percent composition of forbs increasing substantially while the biomass of the shrubs will increase only slightly.
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Five to ten percent of the perennial plants may be dead or dying due to drought or natural senescence at any given time. Dead branched in the creosote bush and occasionally white bursage are common and natural, increasing during drought periods.
Average percent litter cover (%) and depth ( in):
Litter is naturally concentrated under shrubs. Litter from winter spring annual production generally stays in place for several months due to the rock and gravel cover found in interspaces.
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Average annual production on this site is expected to be 75 to 125 lbs/ac. in a year of average precipitation.
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:
Red brome (Bromus rubens, Mediterranean grass, Schismus barbatus, and filaree, Erodium cicutarium may be found on the site in very small amounts (< 1% or < 1 lb/ac.).
Perennial plant reproductive capability:
All plants native to this site are adapted to the climate and are capable of producing seeds, stolons, and/or rhizomes except during the most severe droughts.

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