Ecological site group R008XG153WA
Cool Loamy, threetip sagebrush
Last updated: 09/21/2023
Accessed: 11/21/2024
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): 8 – Columbia Plateau
LRU – Common Resource Areas (CRA):
8.1 - Channeled Scablands
8.2 - Loess Islands
8.3 - Okanogan Drift Hills
8.4 - Moist Pleistocene Lake Basins
8.5 - Moist Yakima Folds
8.7 - Okanogan Valley
Site Concept Narrative:
Diagnostics:
Cool Loamy, threetip sagebrush is an upland sagebrush steppe site occurring on 20 inches and deeper loamy soils. This ecological site occurs principally in two situations: (1) on flat sites at higher elevations and the northern region of MLRA 8, and (2) on north to northeast slopes elsewhere. These sites occur most commonly on silt loam, sandy loam and stony loam soils, but a wide variety of soils and landforms are possible.
As one moves across MLRA 8, the landscape position for Cool Loamy, threetip sagebrush changes. At 10 inches of precipitation Cool Loamy, threetip sagebrush occurs only on the north to northeast slopes. But at 12 inches of precipitation Cool Loamy, threetip sagebrush occurs on all but the south to southwest slopes.
Compared to other upland sites, Cool Loamy, threetip sagebrush has a shift in plant community composition, with threetip sagebrush and Idaho fescue the featured species. Fire tolerant, three-tip sage dominates the reference state shrub layer while Idaho fescue, with or without bluebunch wheatgrass, is dominant in the herbaceous understory. The shrub layer is knee-height three-tip sagebrush with a mix of other shrub species 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.
Daubenmire identified northern Douglas Co., southern Okanogan Co., northern and eastern portion of both Lincoln and Adams counties, for his threetip sagebrush-fescue vegetative 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 allows the shift in major plant species. With higher elevations or northerly facing slopes this ecological site has cooler temperatures year-round and longer lasting snow pack than other MLRA 8 ecological sites. 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. Also, being wetter and cooler, Cool Loamy supports a denser plant cover than the 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
Cool Loamy has cooler temperatures and longer lasting snow than other MLRA 8 ecological sites. Thus, this site supports a denser plant cover and provides water crucial to vegetation when it becomes hot.
Physiographic Features:
The landscape is part of the Columbia basalt plateau. Cool loamy, threetip sagebrush sites are most commonly found on broad ridges, benches and plateaus, stream terraces, drier draw bottoms, north and northeast-facing hillslopes and in small basins.
Physiographic Division: Intermontane Plateau
Physiographic Province: Columbia Plateau
Physiographic Sections: Walla Walla Plateau Section
Landscapes: Hills, valleys and plateaus
Landform: Sideslopes, terraces, benches, alluvial fans
Elevation: Dominantly 600 to 4,200 feet
Central tendency: 1,500 to 3,000 feet
Slope: Total range: 0 to 90 percent
Central tendency: 2 to 30 percent
Aspect: Dominantly northerly aspects, but occurs on all aspects
Geology:
This MLRA is almost entirely underlain by Miocene basalt flows. Columbia River basalt is covered in many areas with as much as 200 feet of loess and volcanic ash. Small areas of sandstones, siltstones, and conglomerates of the Upper Tertiary Ellensburg Formation are along the western edge of this area. Some Quaternary glacial drift covers the northern edge of the basalt flows, and some Miocene-Pliocene continental sedimentary deposits occur south of the Columbia River, in Oregon.
A wide expanse of scablands in the eastern portion of this MLRA, in Washington, was deeply dissected about 16,000 years ago, when an ice dam that formed ancient glacial Lake Missoula was breached several times, creating catastrophic floods. The geology of the northernmost part of this MLRA is distinctly different from that of the rest of the area. Alluvium, glacial outwash, and glacial drift fill the valley floor of the Okanogan River and the side valleys of tributary streams. The fault parallel with the valley separates pre-Tertiary metamorphic rocks on the west, in the Cascades, from older, pre-Cretaceous metamorphic rocks on the east, in the Northern Rocky Mountains. Mesozoic and Paleozoic sedimentary rocks cover the metamorphic rocks for most of the length of the valley on the west.
Climate
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). The climate is characterized by moderately cold, wet winters, and hot, dry summers, with limited precipitation due to the rain shadow effect of the Cascades. Taxonomic soil climate is either xeric (12 – 16 inches PPT) or aridic moisture regimes (10 – 12 inches PPT) with a mesic temperature regime.
Mean Annual Precipitation:
Range: 10 – 16 inches
Seventy to seventy-five percent of the precipitation comes late October through March as a mixture of rain and snow. June through early October is mostly dry.
Mean Annual Air Temperature:
Range: 44 to 54 F
Central Tendency: 48 – 52 F
Freezing temperatures generally occur from late-October through early-April. Temperature extremes are 0 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: 90 to 210
Central tendency: 120 to 160
The growing season for Cool Loamy, threetip sagebrush is April through end of July.
Soil features
Edaphic:
The Cool Loamy, threetip sagebrush ecological site occurs with Loamy, sagebrush, stony and loamy bottom ecological sites.
Representative Soil Features:
This ecological site components are dominantly Typic, Calcic and Vitrandic taxonomic subgroups of Haploxerolls, Durixerolls, Argixerolls and Palexerolls great groups of the Mollisols taxonomic orders. Soils are moderately deep to very deep. Average available water capacity of about 6.0 inches (16.3 cm) in the 0 to 40 inches (0-100 cm) depth range.
Soil parent material is dominantly mixed loess, colluvium and residuum with influence of volcanic ash possible.
The associated soils are Anders, Badge, Bickleton, Conconully, Endicott, Lainand, Linville, Patron, Pushtay, Tanksel and similar soils.
Dominate soil surface is silt loam to very stony fine sandy loamy, with ashy modifier sometimes occurring as well.
Dominant particle-size class is fine to coarse-loamy
Fragments on surface horizon > 3 inches (% Volume):
Minimum: 0
Maximum: 5
Fragments within surface horizon > 3 inches (% Volume):
Minimum: 0
Maximum: 20
Average: 0
Fragments within surface horizon ≤ 3 inches (% Volume):
Minimum: 0
Maximum: 30
Average: 5
Subsurface fragments > 3 inches (% Volume):
Minimum: 0
Maximum: 30
Average: 10
Subsurface fragments ≤ 3 inches (% Volume):
Minimum: 0
Maximum: 40
Average: 10
Drainage Class: Dominantly 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 to moderately low
10 to 40 inches: Moderately high to moderately low
Depth to root-restricting feature (inches):
Minimum: 20
Maximum: Greater than 60 inches
Electrical Conductivity (dS/m):
Minimum: 0
Maximum: 4
Sodium Absorption Ratio:
Minimum: 0
Maximum: 0
Calcium Carbonate Equivalent (percent):
Minimum: 0
Maximum: 25
Soil Reaction (pH) (1:1 Water):
0 - 10 inches: 5.6 to 9.0
10 - 40 inches: 5.6 to 9.0
Available Water Capacity (inches, 0 – 40 inches depth):
Minimum: 1.4
Maximum: 9.7
Average: 6.0
Vegetation dynamics
Ecological Dynamics:
Cool Loamy, threetip sagebrush produces about 800-1200 pounds/acre of biomass annually
In the sagebrush steppe areas of MLRA 8, Wyoming sagebrush – bluebunch wheatgrass communities reign far and wide. But Cool Loamy, threetip sagebrush has a shift in plant community composition, with threetip sagebrush and Idaho fescue the featured species. Bluebunch wheatgrass and threadleaf sedge are also important species on this site.
Compared to other upland ecological sites, Cool Loamy, threetip sagebrush has more available soil moisture. This happens twofold: (1) there is more moisture (more spring rain, deeper snowpack, more fog), and (2) the precipitation is more effective (cooler temperatures, less runoff and less evaporation due to closer spacing of plants, and hence, more soil cover). 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 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.
Both 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. These roots create a massive underground source to stabilize the soils, provide organic matter and nutrients inputs, and help maintain soil pore space for water infiltration and water retention in the soil profile. The extensive rooting system of mid-sized bunchgrasses leave very little soil niche space available for invasion by other species. This drought resistant root can compete with, and suppress, the spread of exotic weeds.
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.
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 that the community remains resistant to medusahead invasion if the site maintains 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 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. Under windy conditions, a fire can burn into the crown of Idaho fescue, leaving behind “black holes” or nothing but ash. When a site loses its Idaho fescue, the holes will be filled by vigorous native species or exotic weeds. Threetip sage and bluebunch wheatgrass keeps the site resistant to change, while Idaho fescue makes the site more at risk.
A severe fire puts stress on the entire community. The sagebrush layer is completely removed. 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 will 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 threetip sage increase
3. Both Idaho fescue and bluebunch wheatgrass decline while threetip sage and threadleaf sedge increase
4. With further decline invasive species 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 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 top growth: (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,
(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.
Supporting Information:
Associated Sites:
Cool Loamy, threetip sagebrush in MLRA 8 is associated with other sites in the Sagebrush Steppe area of MLRA 8 including, Loamy, Stony, Stony Foothills, Stony Foothills South Slope
Similar Sites:
Cool Loamy, threetip sagebrush in MLRA 8 has threetip sage with Idaho fescue and bluebunch wheatgrass. Cool Loamy in MLRA 7 Columbia Basin is similar but with less threetip sage and Idaho fescue. The Channel Scabland area on MLRA 9 Palouse Prairie also has a similar Cool Loamy ecological site.
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 008X
Columbia Plateau
Subclasses
Stage
Provisional
Contributors
Provisional Site Author: Kevin Guinn
Technical Team: K. Moseley, G. Fults, R. Fleenor, W. Keller, C. Smith, K. Bomberger, C. Gaines, K. Paup-Lefferts
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