Ecological site group R009XG626WA
Stony South Aspect
Last updated: 11/22/2023
Accessed: 12/05/2024
Ecological site group description
Key Characteristics
None specified
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.
Physiography
Hierarchical Classification
Major Land Resource Area (MLRA): 9 – Palouse and Nez Perce Prairie
LRU – Common Resource Areas (CRA):
9.1 - Channeled Scablands
9.12 - Moist Loess Islands
9.2 - Palouse Hills
9.3 - Dissected Loess Uplands
9.4 - Deep Loess Foothills
9.5 - Warm Canyons and Dissected Uplands
Site Concept Narrative:
Diagnostics:
Stony South Slope is an upland, bunchgrass-forb, grassland site occurring on south facing slopes. Soils are moderately deep (20-40”) and stony to extremely stony. Soils have a stony or cobbly surface and rock fragments (35% or more) throughout the profile. Soils are generally loam or silt loam over clay loam and clay.
Perennial bunchgrasses dominate the reference state while native forbs fill the interspecies. Shrubs are minor to nonexistent. Bluebunch wheatgrass is the dominant bunchgrass in the top grass layer, while Sandberg bluegrass is the major grass of the lower grass layer. Lupine, balsamroot, biscuitroot and phlox are common forbs.
Principle Vegetative Drivers:
The soil depth (20-40”) is not overly limiting to most plant roots. Stones throughout the profile limit water holding capacity some, but also make for good water drainage so this site doesn’t stay in an anaerobic condition very long which is good for a wide variety of upland plants.
The two big vegetative drivers are the south aspect and spring rains. This site receives a lot of solar radiation and is not very well suited for more mesic species such as Idaho fescue. The spring rain ensures that the vegetation production for this site is in excess of 1000 pounds annually.
Influencing Water Features:
A plant’s ability to grow on a site and overall plant production is determined by soil-water-plant relationships:
1. Whether rain and melting snow runs off-site or infiltrates into the soil
2. Whether soil condition remain aerobic or become saturated and become anaerobic
3. Water drainage and how quickly the soil reaches wilting point
With adequate cover of live plants and litter, there are no restrictions on this ecological site with water infiltrating into the soil. In some years Shallow Stony sites can become saturated due to the shallow soil depth, but with good drainage would remain anaerobic for only a short period of time. This site has an extremely restricted water holding capacity, so plant production is quite limited.
Physiographic Features:
MLRA 9 is south of the Okanogan Highlands and Spokane Valley, east of the Columbia Basin, includes only the wet end of the Channeled Scablands and forms a horseshoe around the Blue Mtns. The landscape is part of the Columbia basalt plateaus and Northern Rocky foothills. Stony South Slope occurs on south facing hillslopes, mountain sideslopes and canyon walls.
MLRA 9 has three distinct geographical types:
(1) the Palouse Hills on the east side
(2) the loess hills to the south and west
(3) the Channeled Scabland-loess islands in the northwest
Physiographic Division: Intermontane Plateau and Northern Rocky Mountain System
Physiographic Province: Columbia Plateau and Northern Rocky Mountains
Physiographic Sections: Walla Walla Plateau and Blue Mountain Section
Landscapes: Hills, plateaus and mountains
Landform: Sideslopes, hillslopes, ridges
Elevation: Dominantly 1,000 to 5,500 feet
Slope: Total range: 0 to 90 percent
Central tendency: 30 to 50 percent
Aspect: Dominantly southern aspects
Geology:
MLRA 9 is almost entirely underlain by Miocene basalt flows. Columbia River basalts are covered by wind-blown loess and volcanic ash with a thickness up to 250 feet thick. The oldest layer of loess accumulated between 2 and 1 million years ago, while the uppermost layers of Palouse Loess accumulated between 15,000 years ago and modern times. The mid layers of loess were deposited episodically between 77,000 years and 16,000 years ago. During the Pleistocene era the channeled scablands, the northwest portion of MLRA 9, were scoured of topsoil by the Lake Missoula Floods about 15,000-17,000 years ago. Flows removed topsoil from exposed ridges and basalt rims in canyons.
Climate
The climate across MLRA 9 is characterized by moderately cold, wet winters, and relatively dry summers.
Mean Annual Precipitation:
Range: 16 – 28 inches
Winter precipitation, primarily snow, occurs during low-intensity, Pacific-frontal storms. During winter these storms produce occasional rains that fall on frozen or thawing ground surfaces. High intensity, convective thunderstorms produce some rain during the growing season. Precipitation is evenly distributed throughout fall, winter and spring.
Mean Annual Air Temperature:
Range: 40 to 52 F
Central Tendency: 44 – 49 F
Freezing temperatures generally occur from late-October through early-April. Temperature extremes are -10 degrees in winter and 110 degrees in summer. Winter fog is variable and often quite localized, as the fog settles on some areas but not others.
Frost-free Period (days):
Total range: 60 to 180
Central tendency: 100 to 140
The growing season for Stony South aspect is generally March through July.
Soil features
Edaphic:
The Stony South Aspect ecological site commonly occurs with rock outcrop, Shallow Stony, Very Shallow and one of the Loamy ecological sites. Soils are formed in loess and ash mixed with residuum, colluvium, alluvium and tuff weathered from basalt. Soils and both shallow and stony.
Representative Soil Features:
This ecological site components are dominantly Typic and Lithic taxonomic subgroups of Argixerolls and Haploxerolls great groups of the Mollisols. Soils are shallow to very deep. Average available water capacity of about 1.8 inches (4.6 cm) in the 0 to 40 inches (0-100 cm) depth range.
Soil parent material is dominantly loess and colluvium derived from basalt, possibly mixed with minor amounts of ash in the upper part of the soil.
The associated soils are Gwinly, Laufer, Limekiln and similar soils.
Dominate soil surface is gravelly silt loam to very stony loam.
Dominant particle-size class is loamy to clayey-skeletal.
Fragments on surface horizon > 3 inches (% Volume):
Minimum: 0
Maximum: 5
Fragments within surface horizon > 3 inches (% Volume):
Minimum: 0
Maximum: 30
Average: 15
Fragments within surface horizon ≤ 3 inches (% Volume):
Minimum: 0
Maximum: 30
Average: 15
Subsurface fragments > 3 inches (% Volume):
Minimum: 10
Maximum: 40
Average: 20
Subsurface fragments ≤ 3 inches (% Volume):
Minimum: 0
Maximum: 30
Average: 20
Drainage Class: Well drained
Water table depth: Greater than 60 inches
Flooding:
Frequency: None
Ponding:
Frequency: None
Saturated Hydraulic Conductivity Class:
0 to 10 inches: Moderately high
10 to 40 inches: Moderately high to moderately low
Depth to root-restricting feature (inches):
Minimum: Greater than 60
Maximum: Greater than 60
Electrical Conductivity (dS/m):
Minimum: 0
Maximum: 10
Sodium Absorption Ratio:
Minimum: 0
Maximum: 10
Calcium Carbonate Equivalent (percent):
Minimum: 0
Maximum: 40
Soil Reaction (pH) (1:1 Water):
0 - 10 inches: 6.1 to 8.4
10 - 40 inches: 6.1 to 9.0
Available Water Capacity (inches, 0 – 40 inches depth):
Minimum: 0.9
Maximum: 2.7
Average: 1.8
Vegetation dynamics
Ecological Dynamics:
Stony South aspect produces about 750-1250 pounds/acre of biomass annually.
Stony South Slope is a bunchgrass-forb ecological site. The climax condition consists of bluebunch wheatgrass plants and vernal forbs, particularly in years of above-normal precipitation. Idaho fescue and shrubs have a minor role in this site. Six weeks fescue and Sandberg bluegrass are typical early spring species.
Bluebunch wheatgrass is a long-lived, mid-sized bunchgrass with an awned or awnless seed head arranged in a spike. In healthy communities, bluebunch wheatgrass provides a crucial and extensive network of roots to the upper portions (up to 48” deep in soils with no root-restrictive horizons) of the soil profile. This root-network stabilizes the soils, provides organic matter and nutrients, and helps to maintain soil pore space for water infiltration and retention un the soil profile. The extensive rooting system of mid-sized grasses leave very little space for invasion by other species. This drought resistant root mass can compete with, and suppress, the spread of exotic weeds.
The stability and resiliency of the reference communities is directly linked to the health and vigor of bluebunch wheatgrass. Refer to page 8 for more details about bluebunch physiology. Research has found, on similar rangeland, that communities remain resistant to medusahead if sites maintain at least 0.8 mid-sized bunchgrass plant/sq. ft. (K. Davies, 2008). The relationship between bunchgrasses and other invasive species should be similar. It is bluebunch that holds the system together. If we lose the bluebunch the ecosystem crashes or unravels.
Stony south aspect has some inherent protection from some disturbances but also has inherent vulnerability from other disturbances. The steep slopes and surface stones do provide a little protection from grazing as these are not the first sites selected by livestock and game animals. Fire can race uphill as the flames are always burning into uphill foliage. All things considered Stony South Slope are less stable than Shallow Stony. Ecological sites
The natural disturbance regime for grassland communities is periodic lightning-caused fires. Ponderosa pine communities have the shortest Fire Return Interval (FRI) of about 10-20 years (Miller). The FRI increases as one moves to wetter forested sites or to drier shrub steppe communities. The FRI listed in research for sagebrush steppe communities is quite variable. Given the uncertainties and opinions of reviewers, a mean of 75 years was chosen for Wyoming sagebrush communities (Rapid Assessment Model). This would place the historic FRI for grassland steppe at 30-50 years perhaps, and even as short as 5-10 years in some locations.
The effect of fire on the community depends upon both the severity and season of the burn. See Vallentine’s Range Improvement for more detail. With a light to moderate fire there can be a mosaic of burned and unburned patches. The perennial grasses thrive as the fire does not get into the crown. With adequate soil moisture bunchgrasses can make tremendous growth the year after the fire.
Even a fire that is severe on many ecological sites, may flash over a Stony South Slope hillside quickly. Also, most fires happen after the end of wildflower season, thus forbs are unaffected. So, these bluebunch wheatgrass communities with none to very little Idaho fescue, are largely unaffected by fire.
Grazing is another common disturbance that occurs to this ecological site. Grazing pressure can be defined as heavy grazing intensity, or frequent grazing during reproductive growth, or season-long grazing (the same plants grazed more than once). As grazing pressure increases the plant community unravels in stages:
1. Bluebunch wheatgrass declines while Sandberg bluegrass and unpalatable forbs increase
2. With further decline invasive species such as cheatgrass, bulbous bluegrass and tarweed colonize the site
3. As the community of native perennials weaken the alien species take their place. This happens progressively until the invasive species dominate the site.
For more grazing management information refer to Range Technical Notes found in Section I Reference Lists of NRCS Field Office Technical Guide for Washington State.
In Washington, bluebunch wheatgrass communities provide habitat for a variety of upland wildlife species.
Supporting Information:
Associated Sites:
Stony South Aspect is associated with other ecological sites in MLRA 9, including Very Shallow, Shallow Stony, Loamy bunchgrass and North Aspect bunchgrass,
Similar Sites:
This MLRA 9 Stony South Aspect site extends into MLRA 43c the Blur mountains.
Inventory Data References (narrative):
Data to populate Reference Community came from several sources: (1) NRCS ecological sites from 2004, (2) Soil Conservation Service range sites from 1980s and 1990s, (3) Daubenmire’s habitat types, and (4) ecological systems from Natural Heritage Program
Major Land Resource Area
MLRA 009X
Palouse and Nez Perce Prairies
Subclasses
Stage
Provisional
Contributors
Kevin Guinn, C. Smith, R. Fleenor, K. Paup-Lefferts
Click on box and path labels to scroll to the respective text.
Ecosystem states
T1 | - | grazing pressure |
---|---|---|
T2 | - | grazing pressure |
State 1 submodel, plant communities
1.1a | - | grazing pressure |
---|---|---|
1.2a | - | improved grazing management |