Ecological site R030XB108NV

R029XY077NV	SHALLOW GRAVELLY LOAM 8-10 P.Z.
R030XB051NV	UPLAND WASH
R030XB075NV	GRAVELLY FAN 5-7 P.Z.
R030XB107NV	COARSE GRAVELLY LOAM 5-7 P.Z.
R030XB134NV	QUARTZITE OUTWASH

R030XB090NV	GRAVELLY FAN 7-9 P.Z. BOER4 major grass
R030XB014NV	SHALLOW GRAVELLY LOAM 7-9 P.Z. Less productive site; BOER4 major grass
R030XB107NV	COARSE GRAVELLY LOAM 5-7 P.Z. Less shrub diversity, less productive site
R030XB051NV	UPLAND WASH CORA minor spp., if present
R030XB057NV	SHALLOW GRANITIC LOAM 5-7 P.Z. soils derived from granitic parent materials
R030XB015NV	SHALLOW GRAVELLY SLOPE 7-9 P.Z. Less productive site; BOER4 major grass

Tree	Not specified
Shrub	(1) Coleogyne ramosissima
Herbaceous	(1) Pleuraphis rigida

Landforms	(1) Inset fan
Elevation	3600 – 5000 ft
Slope	2 – 15 %

Frost-free period (average)	210 days
Freeze-free period (average)
Precipitation total (average)	10 in

Drainage class	Well drained
Permeability class	Moderately rapid

Ecological dynamics

Please refer to group concept R030XB108NV to view the provisional STM.

As ecological condition deteriorates, perennial grasses and forbs decrease as woody species increase. Following wildfire, blackbrush is removed from the community as perennial grasses and shrubs such as Mojave desertrue, white burrobrush, and spiny horsebrush increase. Introduced annual forbs and grasses readily invade this site.

Fire Ecology:
Low amounts of fine fuels in interspaces probably limited fire spread to only extreme fire conditions, during which high winds, low relative humidity, and low fuel moisture led to high intensity stand-replacing crown fires. Historical fire return intervals appear to have been on the order of centuries, allowing late seral blackbrush stands to reestablish. Blackbrush stands are subject to fire, and fire will start and spread easily due to the dense, close spacing nature and resinous foliage of blackbrush. Blackbrush is slow to reestablish. Fourwing saltbush is most common under regimes of infrequent fire and moderate browsing. Fire top-kills or kills fourwing saltbush, depending upon ecotype. Fourwing saltbush may sprout after top-kill. Winterfat is either killed or top-killed by fire, depending on fire severity. Severe fire can kill the perennating buds located several inches above the ground surface and thus kills the plant. In addition, severe fire usually destroys seed on the plant. Low-severity fire scorches or only partially consumes the aboveground portions of winterfat and thus does not cause high mortality. Fires in spiny hopsage sites generally occur in late summer when plants are dormant, and sprouting generally does not occur until the following spring. Spiny hopsage is considered to be somewhat fire tolerant and often survives fires that kill sagebrush. Mature spiny hopsage generally sprout after being burned. Spiny hopsage is reported to be least susceptible to fire during summer dormancy. Spiny menodora often survives fire because its foliage does not readily burn. Fire most likely top-kills big galleta. Big galleta sprouts from rhizomes following fire. Damage to big galleta from fire varies, depending on whether big galleta is dormant when burned. If big galleta is dry, damage may be severe. However, when plants are green, fire will tend to be less severe and damage may be minimal, with big galleta recovering quickly. 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.

State and transition model

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Click on state and transition labels to scroll to the respective text

Ecosystem states

1. Reference Plant Community

State 1 submodel, plant communities

1.1. Reference Plant Community

State 1
Reference Plant Community

Community 1.1
Reference Plant Community

The reference plant community is dominated by blackbrush. Winterfat, spiny hopsage, fourwing saltbush, and spiny menodora are other important species associated with this site.
Potential vegetative composition is about 15% grasses, 5% annual and perennial forbs and 80% shrubs. Approximate ground cover (basal and crown) is 30 to 40 percent.

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	320	480	640
Grass/Grasslike	60	90	120
Forb	20	30	40
Total	400	600	800

Additional community tables

Table 6. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production ()	Foliar cover (%)
Grass/Grasslike
1	Primary Perennial Grasses			24–120
	desert needlegrass	ACSP12	Achnatherum speciosum	12–60	–
	big galleta	PLRI3	Pleuraphis rigida	12–60	–
2	Secondary Perennial Grasses			1–48
	Indian ricegrass	ACHY	Achnatherum hymenoides	3–20	–
	threeawn	ARIST	Aristida	3–20	–
	low woollygrass	DAPU7	Dasyochloa pulchella	3–20	–
	squirreltail	ELEL5	Elymus elymoides	3–20	–
3	Annual Grasses			1–18
	sixweeks grama	BOBA2	Bouteloua barbata	3–20	–
Forb
4	Perennial forbs			12–48
	desert globemallow	SPAM2	Sphaeralcea ambigua	3–12	–
5	Annual forbs			1–30
Shrub/Vine
6	Primary shrubs			312–534
	blackbrush	CORA	Coleogyne ramosissima	240–300	–
	fourwing saltbush	ATCA2	Atriplex canescens	12–48	–
	winterfat	KRLA2	Krascheninnikovia lanata	12–48	–
	desertsenna	SEAR8	Senna armata	12–48	–
	Shockley's goldenhead	ACSH	Acamptopappus shockleyi	12–30	–
	spiny menodora	MESP2	Menodora spinescens	12–30	–
	spiny hopsage	GRSP	Grayia spinosa	12–30	–
7	Secondary shrubs			30–90
	burrobush	AMDU2	Ambrosia dumosa	6–20	–
	woolly fruit bur ragweed	AMER	Ambrosia eriocentra	6–20	–
	Virgin River brittlebush	ENVI	Encelia virginensis	6–20	–
	jointfir	EPHED	Ephedra	6–20	–
	Eastern Mojave buckwheat	ERFAP	Eriogonum fasciculatum var. polifolium	6–20	–
	burrobrush	HYSA	Hymenoclea salsola	6–20	–
	water jacket	LYAN	Lycium andersonii	6–20	–
	Fremont's dalea	PSFR	Psorothamnus fremontii	6–20	–
	Joshua tree	YUBR	Yucca brevifolia	6–20	–
	Mojave yucca	YUSC2	Yucca schidigera	6–20	–

Location 1: Clark County, NV
Township/Range/Section	T23S R58E S33
General legal description	About 5 miles northwest of Goodsprings, Goodsprings Valley, Clark County, Nevada. This site also occurs in southern Lincoln Counties.

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	08/22/2026
Approved by
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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Natural ResourcesConservation Service

Ecological site R030XB108NV

GRAVELLY INSET FAN 7-9 P.Z.

Last updated: 2/26/2025 Accessed: 08/22/2026

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Table 1. Dominant plant species

Natural Resources
Conservation Service

Last updated: 2/26/2025
Accessed: 08/22/2026