Very Shallow
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
-
Transition T1A
precipitation
More details -
Transition T1B
Extensive spring grazing with heavy use
More details -
Restoration pathway R2A
precipitation
More details -
Transition T2A
Extensive spring grazing
More details -
No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
State 1 Narrative:
The Reference State represents non-invaded communities composed of native species. Invasive annual grasses are not present. Very Shallow sites rarely burn, and in most cases, receives minimal grazing. This ecological site is the most stable ecological site on the landscape.
Reference Community 1.1 is one of four classic Very Shallow communities.
Sandberg bluegrass-stiff sagebrush (only in the Channeled Scabland)
Sandberg bluegrass
Sandberg-bluegrass-one-spike oatgrass
Sandberg bluegrass-bluebunch wheatgrass
So, Community 1.1 is mostly very stable. remaining in State 1 regardless of climate or management. Similarity Index scores are typically higher on Very Shallow than other ecological sites on the landscape.
Community 1.2 represents the heavy forb which is caused by heavy grazing to Sandberg bluegrass and quite rare in MLRA 9. The species are native, but Sandberg bluegrass has a diminished presence and forbs are more prominent. Community 1.2 still has enough Sandberg bluegrass present, to shift back to reference community 1.1, given a change in management.
Reference State Community Phases:
1.1 Reference Short grass – low shrub – mid-grass (variations)
1.2 Heavy Forb Forb – low shrub
Dominant Reference State Species:
Sandberg bluegrass in all variations.
One-spike oatgrass, stiff sagebrush or blue bunchgrass on some sites.
At-risk Communities:
• All communities in the reference state are at risk of moving to State 2. The seed source of cheatgrass and/or ventenata is nearby and blowing onto most sites annually
• Community 1.1 has a high cover of Sandberg bluegrass or with one-spike oatgrass, stiff sagebrush or bluebunch wheatgrass, and is thus, at low risk of moving to State 2, Forb-Annual Grass
• Community 1.2 with less Sandberg bluegrass and more forb cover is more at risk of invasion
Submodel
Description
State 2 Narrative:
This state represents a community that is dominated by invasive annual grasses, broadleaf weeds and unpalatable native forbs.
State 2 is quite rare as most Very Shallow sites never cross the threshold into State 2. They stay at climax or near climax condition, as these sites generally receive limited grazing pressure and rarely burn. The situation below has been witnessed on a couple of ridgetops west of Yakima in MLRAs 6 & 8. Chronic heavy grazing in the spring from migrating elk, feral horses or livestock could cause the following:
• Near elimination of Sandberg bluegrass, resulting in
• A plant community dominated almost exclusively by annual forbs &/or annual grasses.
• Annual grasses were rare in the situations witnessed west of Yakima
The amount of ventenata ebbs and flows depending on precipitation. Ventenata is hardly noticeable during years with below to average precipitation but, dominates the site in the years with above average precipitation.
Higher precipitation Very Shallow sites have been altered by heavy grazing pressure and are dominated by ventenata, medusahead, or bulbous bluegrass. Lomatium or another native forb can be prominent as well. A reduction to Sandberg bluegrass cover allows ventenata and other invasive species the opportunity to colonize and invade on a more permanent basis. Heavy grazing use disrupts the soil surface and the moss-lichen layer via animal hooves, which in turn, causes loss of both soil structure and biological crust. When this happens site resistance to erosional forces are greatly diminished.
State 2 will likely have much less or much more pedestaling than the reference condition. Trampling by livestock or game animals can obliterate pedestals and terracettes. Or, erosion in water flow patterns can cause much more pedestaling than reference condition.
Submodel
Description
State 2 Narrative:
This state represents a community that is dominated by invasive annual grasses, broadleaf weeds and unpalatable native forbs.
State 2 is quite rare as most Very Shallow sites never cross the threshold into State 2. They stay at climax or near climax condition, as these sites generally receive limited grazing pressure and rarely burn. The situation below has been witnessed on a couple of
ridgetops west of Yakima in MLRAs 6 & 8. Chronic heavy grazing in the spring from migrating elk, feral horses or livestock could cause the following:
• Near elimination of Sandberg bluegrass, resulting in
• A plant community dominated almost exclusively by annual forbs &/or annual grasses.
• Annual grasses were rare in the situations witnessed west of Yakima
The amount of ventenata ebbs and flows depending on precipitation. Ventenata is hardly noticeable during years with below to average precipitation but, dominates the site in the years with above average precipitation.
Higher precipitation Very Shallow sites have been altered by heavy grazing pressure and are dominated by ventenata, medusahead, or bulbous bluegrass. Lomatium or another native forb can be prominent as well. A reduction to Sandberg bluegrass cover allows ventenata and other invasive species the opportunity to colonize and invade on a more permanent basis. Heavy grazing use disrupts the soil surface and the moss-lichen layer via animal
hooves, which in turn, causes loss of both soil structure and biological crust. When this happens site resistance to erosional forces are greatly diminished.
State 2 will likely have much less or much more pedestaling than the reference condition. Trampling by livestock or game animals can obliterate pedestals and terracettes. Or, erosion in water flow patterns can cause much more pedestaling than reference condition.
Submodel
Mechanism
T1A Temporary transition from Reference Community 1.1 to a Temporary Annual Grass Community 2.1. Included is the temporary transition from Heavy Forb Plant Community 1.2 to a Temporary Forb-Annual Grass Plant Community 2.2.
Primary Trigger: years with above average precipitation.
Ecological process: wetter years allow ventenata to dominate the site. Ventenata seed moves onto these sites annually waiting to exploit the next opportunity
Mechanism
Transitions from State to State
T1B This transition is quite rare. This has been witnessed only a couple of times.
Result: Shift from Reference State to State 3 dominated by annual grasses & forbs
Primary Trigger: Extensive spring grazing with heavy use to Sandberg bluegrass or bluebunch wheatgrass. Heavy livestock trailing or trampling of Very Shallow soils by grazing animals could also trigger transition to State 3.
Ecological process: with consistent defoliation pressure Sandberg bluegrass has poor vigor, shrinking crowns and plant mortality. As resources and niche space are released unpalatable forbs increase and invasive species colonize the site. The decline continues until invasive species dominate the site and Sandberg bluegrass has been all but eliminated. The soil is more open to evaporation, to wind and water erosion, and facilitates plant community changes from State 1 to State 3.
Indicators: Declining cover of Sandberg bluegrass, declining soil biotic crust and, increasing gaps between perennial species.
Recovery
State 3 is considered non-reversible. Restoration of Sandberg bluegrass, the low shrub component, native forbs and the soil biotic crust would be very problematic at best on Very Shallow. Seeds must germinate. Seedlings and plugged plants need soil moisture and time to become established. In most years, seeds and plugs may not have a chance as site conditions on Very Shallow can change quickly. Drying winds and bright sun can turn a snowy or muddy site into a hard crust before plants are established. So, the timing of all recovery efforts would have an extremely narrow window of opportunity on Very Shallow.
References:
Boling M., Frazier B., Busacca, A., General Soil Map of Washington, Washington State University, 1998
Daubenmire, R., Steppe Vegetation of Washington, EB1446, March 1968
Davies, Kirk, Medusahead Dispersal and Establishment in Sagebrush Steppe Plant Communities, Rangeland Ecology & Management, 2008
Environmental Protection Agency, map of Level III and IV Ecoregions of Washington, June 2010
Miller, Baisan, Rose and Pacioretty, “Pre and Post Settlement Fire regimes in mountain Sagebrush communities: The Northern Intermountain Region
Natural Resources Conservation Service, map of Common Resource Areas of Washington, 2003
Rapid Assessment Reference Condition Model for Wyoming sagebrush, LANDFIRE project, 2008
Rocchio, Joseph & Crawford, Rex C., Ecological Systems of Washington State. A Guide to Identification. Washington State Department of Natural Resources, October 2015. Pages 156-161 Inter-Mountain Basin Big Sagebrush.
Rouse, Gerald, MLRA 8 Ecological Sites as referenced from Natural Resources Conservation Service-Washington FOTG, 2004
Soil Conservation Service, Range Sites for MLRA 8 from 1980s and 1990s
Vallentine, John F. 1971. Range Development and Improvement. BYU Press, Provo, Utah
Mechanism
R2A Transition from Temporary Plant Community 2.1 back to Reference Community 1.1. Also includes transition back to Degraded Forb Plant Community 1.2 from Plant Community 2.2.
Primary Trigger: years with average and below average precipitation.
Ecological process: native grasses, forbs and shrubs regain competitive advantage and utilize almost all available soil moisture. Ventenata is hardly noticeable.
Mechanism
T2A This transition is a completion of the transition to an invaded state.
Result: Shift from the transitional state of Reference to State 3 dominated by annual
grasses & forbs
Primary Trigger: Extensive spring grazing with heavy use to Sandberg bluegrass or bluebunch wheatgrass. Heavy livestock trailing or trampling of Very Shallow soils by grazing animals could also trigger transition to State 3.
Ecological process: with consistent defoliation pressure Sandberg bluegrass has poor vigor, shrinking crowns and plant mortality. As resources and niche space are released unpalatable forbs increase and invasive species colonize the site. The decline continues until invasive species dominate the site and Sandberg bluegrass has been all but eliminated. The soil is more open to evaporation, to wind and water erosion, and facilitates plant community changes from State 2 to State 3.
Indicators: Declining cover of Sandberg bluegrass, declining soil biotic crust and, increasing gaps between perennial species.
Recovery
State 2 is considered non-reversible. Restoration of Sandberg bluegrass, the low shrub component, native forbs and the soil biotic crust would be very problematic at best on Very Shallow. Seeds must germinate. Seedlings and plugged plants need soil moisture and time to become established. In most years, seeds and plugs may not have a chance as site conditions on Very Shallow can change quickly. Drying winds and bright sun can turn a snowy or muddy site into a hard crust before plants are established. So, the timing of all recovery efforts would have an extremely narrow window of opportunity on Very Shallow.
Model keys
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