Ecological site group R009XG153WA
Cool Loamy, Channeled Scabland
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
Site Concept Narrative:
Diagnostics:
The channeled scabland-loess island region is the only portion of MLRA 9 that is shrub steppe. Cool Loamy occurs on two Common Resource Areas – 9.1 channeled scabland and 9.12 loess islands. This site is also found in Daubenmire’s Threetip Sagebrush-Fescue vegetative zone.
In the reference condition this shrub steppe plant community features threetip sagebrush and Idaho fescue. Fire tolerant, knee-high, three-tip sage dominates the shrub layer while Idaho fescue, with or without bluebunch wheatgrass, is dominant in the herbaceous understory. Cool Loamy has a lush herbaceous component with many perennial forbs.
A mix of other shrub species can be scattered throughout, including Wyoming or basin big sagebrush, rabbitbrush, and horsebrush. The cover of Wyoming and basin sagebrush will depend on how long it has been since the site burned. Snowberry and rose are all but absent from Cool Loamy and the threetip sagebrush-fescue zone.
Principle Vegetative Drivers:
The vegetative expression of this productive site is driven by two factors: (1) moderately deep to deep soil depth provides unrestricted rooting for most species, and (2) the microclimate which favors Idaho fescue. The Channeled Scabland has the coldest winter temperatures in MLRA 9 and a longer lasting snowpack. This site provides crucial water to the vegetation at the hottest time of the growing season, allowing the ecological site more resilience when impacted by disturbances. Cool Loamy supports a denser plant cover than the Loess Hills Loamy ecological site.
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
The Loess Hills Loamy (14-18” PZ) site consists of deep soils and occurs for the most part on gently sloping landforms with little limitations for water infiltration. On steeper slopes and localized high silt or sodic soils, infiltration may be limited. Calcic and petrocalcic horizons may be present indicating long-term moisture penetration. There is generally no run-in moisture from surrounding sites or long-term soil moisture saturation.
Physiographic Features:
The landscape is part of the Columbia basalt plateaus and Northern Rocky foothills. 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.
MLRA 9 has three distinct geographical areas:
(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
Landscapes: plateaus and loess hills
Landform: Dominantly benches, terraces, terraces escarpments
Elevation: Dominantly 1,800 to 3,000 feet
Slope: Total range: 0 to 60 percent
Aspect: Dominantly northern aspects, but can occur on all 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.
The Channeled Scabland was impacted by the Missoula Floods, but the Loess Islands were not inundated or scoured by the floodwaters.
Climate
The channeled scabland region is the coldest and driest part of MLRA 9. The climate across MLRA 9 is characterized by moderately cold, wet winters, and relatively dry summers.
Mean Annual Precipitation:
Range: 14 – 18 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: 42 to 52 F
Central Tendency: 47 to 50 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.
Areas with threetip sagebrush and Idaho fescue when compared to Wyoming sagebrush-bluebunch wheatgrass regions, are cooler from late fall to early spring (October through April), and has higher P (precipitation) and P/T (precipitation-transpiration) for five months (September, November, December, January and March) (Daubenmire).
Frost-Free Period (days):
Total range: 60 to 180
Central tendency: 100 to 140
The growing season for Cool Loamy is April through end of July.
Soil features
Edaphic:
The Cool Loamy channeled scabland ecological site occurs with Stony Foothills, channeled scabland and Very Shallow ecological sites. Cool Loamy channeled scabland is an upland sagebrush-bunchgrass site loamy soil.
Representative Soil Features:
This ecological site components are dominantly Pachic, Typic and Ultic taxonomic subgroups of Argixerolls and Haploxerolls taxonomic great group of the Mollisols taxonomic order but may also include the Vitrandic subgroup. Soils are dominantly very deep. Average available water capacity of about 7 inches (17.8 cm) in the 0 to 40 inches (0-100 cm) depth range.
Soil parent material is dominantly loess, residuum and colluvium.
The associated soils are Thatuna, Tilma, Hesseltine, Hanning and similar soils.
Dominate soil surface is silt loam to stony loam.
Fragments on surface horizon > 3 inches (% Volume):
Minimum: 0
Maximum: 0
Fragments within surface horizon > 3 inches (% Volume):
Minimum: 0
Maximum: 10
Average: 1
Fragments within surface horizon ≤ 3 inches (% Volume):
Minimum: 0
Maximum: 20
Average: 5
Subsurface fragments > 3 inches (% Volume):
Minimum: 0
Maximum: 15
Average: 2
Subsurface fragments ≤ 3 inches (% Volume):
Minimum: 0
Maximum: 30
Average: 10
Drainage Class: Dominantly well drained
Water table depth: Dominantly 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
Depth to root-restricting feature (inches):
Minimum: Dominantly greater than 60, but strongly contrasting textural stratification can occur up to 20 inches occurrences
Maximum: greater than 60
Electrical Conductivity (dS/m):
Minimum: 0
Maximum: 0
Sodium Absorption Ratio:
Minimum: 0
Maximum: 0
Calcium Carbonate Equivalent (percent):
Minimum: 0
Maximum: 0
Soil Reaction (pH) (1:1 Water):
0 - 10 inches: 5.1 to 7.8
10 - 40 inches: 5.6 to 7.8
Available Water Capacity (inches, 0 – 40 inches depth):
Minimum: 3.5
Maximum: 9.3
Average: 7
Vegetation dynamics
Ecological Dynamics:
Cool Loamy, channeled scabland in MLRA 9 produces about 900-1500 pounds/acre of biomass annually
Cool Loamy, channeled scabland is sagebrush steppe with threetip sagebrush and Idaho fescue the featured species. Bluebunch wheatgrass and threadleaf sedge are also important species on this site.
Compared to the Loamy, bunchgrass, 15-18” ppt., Cool Loamy, channeled scabland of the channel scabland has more available soil moisture as the season gets hotter. With cooler temperatures, less runoff and less evaporation the precipitation on Cool Loamy is more effective. Threetip sage and Idaho fescue are especially linked to the additional soil moisture on this ecological site. The third dominant species in the reference state, bluebunch wheatgrass, is not as linked to the additional soil moisture.
Threetip sagebrush is a short, shallow-rooted, evergreen shrub. Leaves are more deeply lobed than big sagebrush. Compared to big sagebrush, threetip sage grows on sites that are moister, north slopes or at higher elevations. Threetip sagebrush has a very slow growth rate, reaching a height of one foot after twenty years. In Washington threetip sage generally sprouts following fire but it is not a big-time sprouter like rabbitbrush. It can take years for threetip sage to get back to pre-burn conditions.
Idaho fescue is shorter and has a dense clump of shoots, while bluebunch wheatgrass is taller and is less dense. Both species are long-lived bunchgrasses. Bluebunch has an awned or awnless seed head arranged in a spike, while Idaho fescue has an awned seed head arranged in a panicle. The ratio of Idaho fescue to bluebunch wheatgrass plants on any site can vary due to aspect and elevation.
Threadleaf sedge is a sod-forming, densely tufted, native perennial graminoid. In nature threadleaf sedge seedlings are rare as it reproduces mainly from asexual tillers. Often threadleaf sedge is an increaser when other species in the community are in decline.
In healthy communities, these mid-sized grasses provide 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 Idaho fescue and bluebunch wheatgrass. Refer to page 8 for more details about bunchgrass 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). These two bunchgrasses hold the system together. If we lose either or both bunchgrass the ecosystem begins to unravel.
The natural disturbance regime for grassland communities is periodic lightning-caused fires. The fire return intervals (FRI) listed in research for sagebrush steppe communities is quite variable. Ponderosa pine communities have the shortest FRI of about 10-20 years (Miller). The FRI increases as one moves to wetter forested sites or to dries shrub steppe communities. Given the uncertainties and opinions of reviewers, a mean of 75 years and a range of 50-100 was chosen for Wyoming sagebrush communities (Rapid Assessment Model). Threetip sage-fescue areas should have a comparable fire return interval.
Some fires are spotty or do not burn hot enough to fully remove the sagebrush. Fires with light severity will remove less sagebrush and open smaller patches for grass and forb recovery, whereas the more severe fires will remove almost all the sagebrush and leave vast areas open to return to bunchgrass dominance. This is how the patchy distribution occurs. Rabbitbrush and horsebrush are sprouting shrubs and may also increase following fire.
The effect of fire on the main species is mixed for the Cool Loamy, channeled scabland site. Threetip sagebrush in Central Washington sprouts from lateral roots or the root crown following fire and bluebunch wheatgrass is fire tolerant. Threetip is also a vigorous, wind-dispersed seeder. And in many cases, after fire, threetip will both re-sprout and disperse new seed from the surviving plants. Both species recover quickly. But Idaho fescue is much more sensitive to fire. Threetip sage and bluebunch wheatgrass keep the site resistant to change, while Idaho fescue makes the site more at risk.
A severe fire puts stress on the entire community. The Wyoming sagebrush layer is completely lost. Spots or patches with heavy sagebrush are sterilized by the fire and must be seeded to prevent invasive species (annual grasses, tumble mustard) from totally occupying the site. Bluebunch wheatgrass and basin wildrye may have weak vigor for a few years but generally survive. Idaho fescue plants are very much at risk with a severe burn coupled with wind. The result can be “black holes” or ash 2-3 inches into the crown. The death of Idaho fescue plants creates holes in the community, and the opportunity for exotic species to colonize. Needle and thread is one native species that can increase via new seedlings.
Idaho fescue and bluebunch wheatgrass exhibit rapid tillering when there is light severity fires and favorable soil moisture. But, the longer the site goes without fire and the more grazing pressure added, the more threetip sagebrush cover increases and the bunchgrasses decline.
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. Cusick bluegrass is eliminated. Adjacent natives fill the void
2. Idaho fescue declines while bluebunch wheatgrass and threadleaf sedge increase
3. Both Idaho fescue and bluebunch wheatgrass decline. Threadleaf sedge, Sandberg bluegrass, Nelson needlegrass and woolly plantain increase
4. With further decline invasive species such as Japanese brome and cheatgrass colonize the site
5. The site can become a threetip sage-threadleaf sedge community
Managing sagebrush steppe to improve the vigor and health of native bunchgrasses begins with an understanding of grass physiology. New growth each year begins from basal buds. Given the opportunity Idaho fescue readily produces new seedlings while bluebunch wheatgrass plants rely principally on tillering. During seed formation, the growing points of bluebunch wheatgrass become elevated and are vulnerable to damage or removal. Idaho fescue has weak stems, and is thus, much more sensitive to grazing than bluebunch wheatgrass.
If defoliated during the formation of seeds, bluebunch wheatgrass has limited capacity to tiller compared with other, more grazing resistant grasses (Caldwell et al., 1981). Repeated critical period grazing is especially damaging. Over several years each native bunchgrass pasture should be rested during the critical period two out of every three years (approximately April 15 – July 15). And each pasture should be rested the entire growing-season every third year (approximately March 1 – July 15).
In the spring each year it is important to monitor and maintain an adequate topgrowth: (1) so plants have enough energy to replace basal buds annually, (2) to optimize regrowth following spring grazing, (3) to protect the elevated growing points of bluebunch wheatgrass, and (4) to avoid excessing defoliation of Idaho fescue with its weak stems.
These grasses remain competitive if:
(1) Basal buds are replaced annually, and Idaho fescue produces seed and,
(2) Enough top-growth is maintained for growth and protection of growing points, and
(3) The timing of grazing and non-grazing is managed over a several-year period. Careful management of late spring grazing is especially critical
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, threetip sagebrush – Idaho fescue/bluebunch wheatgrass communities provide habitat for a variety of upland wildlife species such as sharp-tail grouse.
Supporting Information:
Associated Sites:
Cool Loamy, channeled scabland is associated with Very Shallow and Stony Foothills.
Similar Sites:
Cool Loamy, channeled scabland has threetip sage with Idaho fescue and bluebunch wheatgrass. MLRA 8 Columbia Plateau has a comparable Cool Loamy site. MLRA 7 Columbia Basin Cool Loamy has less Idaho fescue and less threetip sage.
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, Technical Team: R. Fleenor, K. Paup-Lefferts, W. Keller
Click on box and path labels to scroll to the respective text.
Ecosystem states
T1 | - | Heavy grazing pressure |
---|---|---|
R1 | - | restoration |
T2 | - | heavy grazing pressure |
State 1 submodel, plant communities
1.1a | - | grazing pressure |
---|---|---|
1.2a | - | Moderate severity fire |
State 2 submodel, plant communities
State 3 submodel, plant communities
3.1a | - | Grazing pressure |
---|---|---|
3.2a | - | shrub control and seeded |