Very Shallow
Scenario model
Current ecosystem state
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Management practices/drivers
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- Transition T1A More details
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
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, receive minimal grazing. This ecological site is the most stable ecological site on the landscape. The Reference state has 2 communities: 1.1 Sandberg Bluegrass and Low Shrub and 1.2 Forb and Low Shrub. The Reference state species include Sandberg bluegrass, stiff sagebrush, and/or other low-shrub Eriogonum species
At-risk Communities: • All communities in the Reference state are at risk of moving to State 2. The seed source of cheatgrass is nearby and blowing onto most sites annually • Community 1.1 has a high Sandberg bluegrass cover and is thus, at lower risk of moving to State 2, Forb-Annual Grass • Community 1.2, has less Sandberg bluegrass cover and a high amount of forb cover, and is at considerable risk of moving to State 2
Submodel
Description
Narrative: This state represents the ecological changes that occur when there is a shift from dominance by perennial native grasses to forbs or annual grass dominance in the herbaceous layer. The shrub components generally remain in the overstory. Most Very Shallow sites never cross the threshold into State 2 as they are not attractive to grazing animals and rarely burn (limited forage values and surface rocks). The exception being chronic heavy grazing in the spring from migrating elk, feral horses or livestock. As the cover of Sandberg bluegrass significantly declines the site becomes open to invasion by invasive annuals, however. Invasive annual grasses, which are common & frequently dominant on adjacent Loamy ecological sites, do not often compete as well on Very Shallow sites. However, the cheatgrass seed blows onto Very Shallow sites annually and can become a minor component. In a year with heavy snowfall and early spring rain, such as 2017, the site had far more moisture than the plant community could utilize. This is the perfect opportunity for cheatgrass seed, which is capable of rapid germination and growth to establish in significant amounts across the site. In the following years when moisture is normal or below normal, native species will utilize most of the available moisture and cheatgrass seed will not germinate or make viable plants. Therefore, in most cases, these micro-bursts of cheatgrass tend to be episodic and mostly a temporary condition on Very Shallow sites. However, due to long-term disturbances and higher precipitation, Very Shallow sites in the Goldendale Prairie portion of MLRA 8 are now dominated by cheatgrass, medusahead, ventenata, or bulbous bluegrass. Sites have been significantly impacted by heavy grazing pressure from livestock that have removed much of the native grass components, leaving niches for these invasive annuals to take hold. Native forbs such as Lomatium may be prominent, but the grass component has shifted completely. A reduction in Sandberg bluegrass cover allows annual grasses 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 is greatly diminished as well. State 2 may exhibit either a significant decrease in pedestaling due to the lack of bunchgrass cover and heavy use trampling by ungulates, or there will be a significant increase in pedestaling due to increased erosion from water flows around the remaining bunchgrasses. Communities for State 2: Community 2.1: dominated by native forbs and/or invasive annual grasses. Forbs that increase in the altered conditions and are competitive with invasive grasses, can include lomatium, fleabane (Erigeron sp.), willowherb (Epilobium sp.), yarrow (Achillea millefolium), and onion (Allium sp.). Typical invasive grasses may include annual bromes, medusahead, and sixweeks fescue (Vulpia octoflora).
State 2 is considered non-reversible. Restoration of Sandberg bluegrass, the low shrub component, native forbs, and the soil biotic crust would be extremely difficult, labor intensive, and costly. Seedlings and plugged plants need soil moisture and time to germinate and become established. In most years, seeds and plugs may not have a chance as site conditions on Very Shallow can change quickly and the non-native species are much more adaptable under these conditions. Drying winds and bright sun can turn a snowy or muddy site into a hard crust before plants are established. Timing of all recovery efforts would have an extremely narrow window of opportunity on these altered sites of Very Shallow.
Submodel
Mechanism
Result: Shift from Reference Community Phase 1.1 to State 2 Community Phase 2.1, resulting in the shift in functional groups to forbs and non-native annual grass dominance. Primary Trigger: Extensive spring grazing with heavy use to Sandberg bluegrass. The grazing pressure can come from elk, cattle or feral horses. Secondary Trippers: a micro-burst of cheatgrass could put Community 1.2 at risk. The trampling of Very Shallow soils, displacing and disturbing the surface soil structure by grazing animals could also trigger transition to State 2. A micro-burst of annual grasses could allow even pristine sites to be invaded. Community 1.2 is the community most at risk and is also the pathway for crossing the threshold from State 1 to State 2. Ecological process: consistent spring defoliation pressure to Sandberg bluegrass causes poor vigor, shrinking crowns and plant mortality. Most or all Sandberg bluegrass plants are lost from the community, and this allows native forbs to increase and invasive annuals (forbs and grasses) to colonize and expand. This facilitates plant community changes from Community 1.2 to Community 2.1. Indicators: Declining vigor and cover of Sandberg bluegrass, declining soil biotic crust and, increasing gaps between perennial bunchgrasses.
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