Sandstone Upland
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
- Transition T1 - 2 More details
- Transition T1 - 3 More details
- Transition T1 - 4 More details
- Restoration pathway R2 - 1 More details
- Transition T2 - 3 More details
- Transition T2 - 4 More details
- Restoration pathway R3 - 1 More details
- Transition T3 - 4 More details
- Restoration pathway R4 - 1 More details
- Restoration pathway R4 - 3 More details
-
No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
The reference state is a combination of several vegetation communities within the Central Appalachian Dry Oak-Pine Forest, the Northeastern Interior Dry-Mesic Oak Forest, and the Central Appalachian Pine-Oak Rocky Woodland Forest Systems as defined by NatureServe (NatureServe 2009). These forests are mostly closed-canopy but can include patches of more open woodlands and grasslands. The coarse, acidic, well drained soils, will host a variable mixture of dry-site oak and pine species. Heath shrubs are common in the understory. Convex, shallow, exposed ridgetop, and rocky areas will tend to have more open canopies and will include pine species and herbaceous species that tolerate very dry conditions. The reference community listed below is one of several that have been documented on the Sandstone Uplands and although it is representative, it is not intended to describe every situation or the full range of conditions for this site.
Submodel
Submodel
Description
The dominance of Pinus Virginiana (Virginia pine) in some areas strongly points to historic agricultural disturbance, or in cleared and/or burned over areas. Oaks may or may not be present. The bare mineral soil of cultivated sites facilitates the germination requirements of Pinus Virginiana, and other early successional species.
Submodel
Mechanism
Logging followed by natural regeneration and fire suppression.
Mechanism
Clearcutting, conversion to agricultural land, then successional forest regrowth.
Mechanism
Clearcutting; tillage; conversion to agricultural land; fertilizer and lime application; active management.
Mechanism
Understory removal to promote growth of oak seedlings; implement a prescribed fire plan; control invasive species.
The following conservation practices from the Natural Resources Conservation Service Field Office Technical Guide can be used for restoration efforts (FOTG-USDA): Brush Management-314; Forest Stand Improvement-666; Herbaceous Weed Control-315; Upland Wildlife habitat management-645; Prescribed burning-338.
Relevant conservation practices
Practice | External resources |
---|---|
Brush Management |
|
Prescribed Burning |
|
Upland Wildlife Habitat Management |
|
Forest Stand Improvement |
|
Herbaceous Weed Control |
Mechanism
Clearcutting, conversion to agricultural land, then successional forest regrowth.
Mechanism
Clearcutting; tillage; conversion to agricultural land; fertilizer and lime application; active management.
Mechanism
Remove understory, plant native seeds and seedlings, eliminate and manage nonnative species, implement a prescribed fire plan. Return to the reference or post logged minimally managed state may require a very long term series of costly management options and stages. Many species may need to be planted or seeded to restore the system. Herbivory can be a problem as well as competition from faster growing species. Depending on the existing seed bank and the proximity of a mature forest from which to recruit seeds, ruderal forests may regain a mixed forest stand. Nevertheless, sites that have been cleared and tilled have significant soil disturbance which may include compaction, erosion, loss of native soil structure, loss of soil organic matter, disruption of soil microorganisms, all which affect the soil’s nutrient availability and water holding capacity (Duiker and Myers, 2005). These characteristics favor recolonization by plant species that have wind dispersed seeds (verses those that propagate through underground roots called rhizomes, or which have heavy seeds that stay near the parent tree), are shade intolerant, have rapid to moderate growth rates, and drought tolerance (Dyer, 2010). Aggressive control of nonnative species and invasive species will be ongoing.
The following conservation practices from the Natural Resources Conservation Service Field Office Technical Guide can be used for restoration efforts (FOTG-USDA): Brush Management-314; Critical Area Planting-342; Early Successional Habitat Development-647; Fence-382; Forest Stand Improvement-666; Herbaceous Weed Control-315; Tree/Shrub site Preparation-490; Upland Wildlife habitat management-645; Prescribed burning-338.
Relevant conservation practices
Practice | External resources |
---|---|
Brush Management |
|
Prescribed Burning |
|
Critical Area Planting |
|
Fence |
|
Tree/Shrub Establishment |
|
Upland Wildlife Habitat Management |
|
Early Successional Habitat Development/Management |
|
Forest Stand Improvement |
|
Herbaceous Weed Control |
Mechanism
Clearcutting; tillage; conversion to agricultural land; fertilizer and lime application; active management.
Mechanism
Cease agricultural management, exclude grazing, plant native seeds and seedlings, eliminate and manage nonnative and aggressive species, implement prescribed fire plan. Return to the reference or post logged minimally managed state may require a very long term series of costly management options and stages. Many species may need to be planted or seeded to restore the system. Herbivory can be a problem as well as competition from faster growing species. Depending on the existing seed bank and the proximity of a mature forest from which to recruit seeds, ruderal forests may regain a mixed forest stand. Nevertheless, sites that have been cleared and tilled have significant soil disturbance which may include compaction, erosion, loss of native soil structure, loss of soil organic matter, disruption of soil microorganisms, all which affect the soil’s nutrient availability and water holding capacity (Duiker and Myers, 2005). These characteristics favor recolonization by plant species that have wind dispersed seeds (verses those that propagate through underground roots called rhizomes, or which have heavy seeds that stay near the parent tree), are shade intolerant, have rapid to moderate growth rates, and drought tolerance (Dyer, 2010). Aggressive control of nonnative species and invasive species will be ongoing.
The following conservation practices from the Natural Resources Conservation Service Field Office Technical Guide can be used for restoration efforts (FOTG-USDA): Brush Management-314; Critical Area Planting-342; Early Successional Habitat Development-647; Fence-382; Forest Stand Improvement-666; Herbaceous Weed Control-315; Tree/Shrub site Preparation-490; Upland Wildlife habitat management-645; Prescribed burning-338
Relevant conservation practices
Practice | External resources |
---|---|
Brush Management |
|
Prescribed Burning |
|
Critical Area Planting |
|
Fence |
|
Tree/Shrub Site Preparation |
|
Upland Wildlife Habitat Management |
|
Early Successional Habitat Development/Management |
|
Forest Stand Improvement |
|
Herbaceous Weed Control |
Model keys
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