Natural Resources
Conservation Service
Ecological site R015XI104CA
Steep, clayey-skeletal, south-facing slopes
17-19" p.z.
Accessed: 09/23/2026
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Draft. A draft ecological site description is either incomplete or has not undergone quality control and quality assurance review.
Table 1. Dominant plant species
Tree Not specified
Shrub (1) Artemisia californica
(2) Salvia melliferaHerbaceous (1) Nassella pulchra
(2) Nassella lepidaPhysiographic features
This ecological site is found on slopes ranging from 50 to 70% at elevations from 984 to 3280 feet, and is found primarily on south-facing aspects.
Table 2. Representative physiographic features
Landforms (1) Hill
Elevation 984 – 3280 ft Slope 50 – 70 % Aspect SE, S, SW Climatic features
The average annual precipitation in MLRA 15 is from 6 to 20 inches (150 to 510 millimeters) in the area south of San Francisco, and snowfall is rare. The north half of this area can be divided into two rainfall and snowfall zones. The southern half north of San Francisco has an average annual precipitation from 18 to 40 inches (460 to 1,015 millimeters) and snowfall is rare. In the north half, average annual precipitation is from 40 to 79 inches per year (1,015 to 2,010 millimeters) and snowfall is common. Precipitation is evenly distributed throughout fall, winter, and spring but is very low in summer. Coastal areas receive some moisture from fog in summer. Most of the rainfall occurs as low to moderate intensity, Pacific frontal storms during the winter from October to May. The average annual temperature is from 51 to 66 degrees F (10 to 19 degrees C), decreasing from south to north. The average frost-free period is 275 days (180 to 365 days), decreasing with elevation and from south to north.
At Pinnacles National Monument, the average annual precipitation is 17 inches with a range between 17 and 19 inches, mostly from rain in the winter months from November through April. The average annual air temperature is between 59 and 63 degrees Fahrenheit, and the frost-free period (>32F) is 190 to 210 days.
NOTE: Data collected for monthly precipitation and temperatures is only from one climate station.Table 3 Representative climatic features
Frost-free period (average) 210 days Freeze-free period (average) 0 days Precipitation total (average) 20 in BarLineFigure 1. Monthly precipitation range
BarLineFigure 2. Monthly average minimum and maximum temperature
">Influencing water features
Water is not a feature on this ecological site.
Soil features
The soils for this site are derived from residuum weathered from rhyolite, andesite, or from dacite. They are classified as Argixerolls and are found on the moderate to very steep sloping hills around the High Peaks and the Chalone Peaks.
The Argixerolls are shallow to moderately deep soils that are found on south-facing slopes, they experience high evaporation and transpiration, making rainfall much less effective in its soil development. Decomposing plant litter has darkened and softened the surface layer with organic matter that helps retain and recycle the minimal nutrients provided from the acidic parent materials. The winter rainfall has leached clay from the surface layer and transported it down to accumulate in the subsoil, creating a profile that is dark, with a gravelly sandy loam surface layer over bright very cobbly clay loam subsoil over hard bedrock. These soils only store only enough water to support drought-resistant species including coastal scrub species or chamise chaparral, but effectively recycle its minimal nutrients, and shed water for storage downstream.
This ecological site occurs on the following soil components in the Pinnacles National Monument soil survey.
SSA MU Symbol Component name
CA069 106 Argixerolls
Table 4. Representative soil features
Surface texture (1) Gravelly loam
Family particle size (1) Clayey
Drainage class Well drained Permeability class Slow Soil depth 80 – 0 in Surface fragment cover <=3" 30 – 0 % Surface fragment cover >3" 4 – 0 % Available water capacity
(0-40in)0.3 – 0 in Electrical conductivity
(0-40in)0 – 1 mmhos/cm Sodium adsorption ratio
(0-40in)Not specified Soil reaction (1:1 water)
(0-40in)6.6 – 7.3 Subsurface fragment volume <=3"
(Depth not specified)50 – 80 % Subsurface fragment volume >3"
(Depth not specified)0 – 10 % Ecological dynamics
Before European settlement, the natural plant communities for this ecological site range from a California sagebrush and black sage dominated site with very few herbaceous species (also commonly known as coastal scrub) to a native perennial bunchgrasses and perennial and annual forbs site. The reference states for this ecological site are similar to its pre-European state; however the density of the sagebrush and black sage may be different due to fire suppression and the herbaceous species are now heavily dominated by annual grasses and forbs.
The reference state for this ecological site is dominated primarily by California sagebrush (Artemisia californica) and black sage (Salvia mellifera) with California buckwheat (Eriogonum fasciculatum) also commonly present. The herbaceous layer is composed of needlegrasses (Nassella spp.), pine bluegrass (Poa secunda), larkspur (Delphinium spp.), lupine (Lupinus spp.), paintbrush (Castelleja spp.), and wild onions (Allium spp.). Some lesser dominants also include chamise (Adenostoma fasciculatum), foothill pine (Pinus sabiniana), deerweed (Lotus scoparius), monkeyflower (Mimulus spp.), penstemon (Penstemon spp.), phacelias (Phacelia spp.), wooly bluecurls (Trichostema lanatum), and bedstraw (Galium spp.). The non-native annual species that can also be found throughout this site include oats (Avena spp.), bromes (Bromus spp.), annual fescues (Vulpia spp.), and Maltese star-thistle (Centaurea melutinus).
California sagebrush is the key component to the coastal sage scrub plant community, which is composed primarily of unevened-aged stands of low-growing, non-sclerophyllous, shallow-rooted subshrubs (Howard 1993). The coastal sage scrub is found as a plant community mosaic throughout Pinnacles National Monument with the chamise chaparral, blue oak woodlands and annual grasslands. It is found on the steepest portions of the south-facing slopes on shallow, skeletal soils adjacent to the chamise chaparral and across from the blue oak woodlands in the Monument. Coastal sage scrub also commonly consists of black sage, California buckwheat, and deerweed (Lotus scoparius).
California sagebrush is a unique plant that is both a pioneer species and a late seral species. The community boundaries of the coastal sage scrub are considered dynamic, depending on successional patterns influenced by a disturbance; the relative success of different species at establishing seed in the seedbank; and the competitive interactions following a disturbance (Howard 1993). Some research suggests that California sagebrush will invade chamise habitat that has been disturbed, but that most often it’s gradually replaced by chamise in the absence of disturbance. Other research also goes so far as to say that if the disturbances are too frequent, the coastal sage scrub will regress further to annual grassland.
The primary natural disturbance for coastal sage scrub is believed to be fire, although historical documentation of fire in coastal sage scrub is too sparse to allow for estimation of natural fire intervals (Howard 1993). For this ecological site, given it’s proximity to the chamise chaparral plant community, fire intervals would be similar, if not the same at approximately 20 years. The fire intensity is generally higher in the coastal sage scrub than then in the lower seral chamise due to the higher litter accumulations and the higher percentage of terpenes in the scrub vegetation, which would cause them to be more flammable. Light severity fire will top-kill California sagebrush and severe fires will cause plant mortality. However, California sagebrush has adapted itself to fire by sprouting from the root crown in post-fire communities and by establishing seeds that are deeply buried to require charred wood leachate to break dormancy (Howard 1993). Most California sagebrush seed is fire sensitive and their seedbank numbers are moderate, so the seedling densities the first year after fire may be low. Seedling recruitment from sprouts or wind-blown seed disseminated from surviving shrubs is usually good after the first post-fire year, however.
Fire suppression in the coastal sage scrub can create dense stands with little space in between shrubs, which can result in extremely severe, abnormally large fires. Severe fires or fires that occur too frequently would kill the seeds in the seedbank and more than likely diminish the sprouting ability of the current sagebrush on the site, leaving it susceptible to a permanent shift to annual grasslands.State and transition model
Custom diagramStandard diagram
Figure 3. Steep, clayey-skeletal, south-facing slopes
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 textEcosystem states
State 1 submodel, plant communities
State 1
Reference State - Plant Community 2.1Community 1.1
Reference State - Plant Community 2.1This is the reference plant community for the ecological site.
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)Grass/Grasslike 50 100 200 Forb 0 20 50 Total 50 120 250 Table 6. Ground cover
Tree foliar cover 0-0% Shrub/vine/liana foliar cover 30-50% Grass/grasslike foliar cover 20-30% Forb foliar cover 10-20% Non-vascular plants 0% Biological crusts 0% Litter 50-80% Surface fragments >0.25" and <=3" 20-40% Surface fragments >3" 0% Bedrock 0% Water 0% Bare ground 0-10% Table 7. Canopy structure (% cover)
Height Above Ground (ft) Tree Shrub/Vine Grass/
GrasslikeForb <0.5 – – 0-2% 0-5% >0.5 <= 1 – – 15-30% 0-10% >1 <= 2 – 0-10% – – >2 <= 4.5 – 15-50% – – >4.5 <= 13 – 5-10% – – >13 <= 40 0-2% – – – >40 <= 80 – – – – >80 <= 120 – – – – >120 – – – – Additional community tables
Table 8. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Interpretations
Animal community
A large number of specialist and endemic species of plants and animals are found here, including the Quino checkerspot butterfly (Euphydryas editha quino), Hermes copper butterfly (Lycaena hermes), San Diego thorn mint (Acanthomintha ilicifolia), San Diego ambrosia (Ambrosia pumila), San Diego barrel cactus (Ferocactus viridescens), San Diego pocket mouse (Perognathus fallax), Merriam kangaroo rat (Dipodomys merriami), Stephens kangaroo rat (Dipodomys stephensi), red-diamond rattlesnake (Crotalus ruber), San Diego banded gecko (Coleonyx variegatus abbotti), San Diego horned lizard (Phrynosoma coronatum blainvillei), California gnatcatcher (Polioptila californica), and the coastal populations of the cactus wren (Campylorhyncus brunneicapillus).
The ecoregion supports between 150 and 200 species of butterflies, has the highest species richness of native bees in the United States, and has a number of relict species such as the Riverside fairy shrimp (Streptocephalus woottoni), found in vernal pools. The rosy boa (Lichanura trivirgata), California legless lizard (Aniella pulchra), and several relict salamanders are examples of the unusual and distinctive herpetofauna.Supporting information
Inventory data references
ARCA-01 - %
Other references
FEIS: ARCA.
Contributors
K. Moseley
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 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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