Low-Base Chert Exposed Backslope Woodland
Scenario model
Current ecosystem state
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Management practices/drivers
Select a transition or restoration pathway
- Transition T1A More details
- Transition T1B More details
- Transition T1C More details
- Restoration pathway R1B More details
- Transition T2A More details
- Restoration pathway R1A More details
- Transition T3A More details
- Transition T4A More details
- Transition T5A More details
- Restoration pathway T5B More details
- Transition T5A 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The historical reference state for this ecological site was old growth oak woodland. The woodland was dominated by black oak, post oak and white oak. Periodic disturbances from fire, wind or ice maintained the woodland structure and diverse ground flora species. Long disturbance-free periods allowed an increase in both the density of trees and the abundance of shade tolerant species.
Two community phases are recognized in the reference state, with shifts between phases based on disturbance frequency. Unaltered reference sites are rare today. Many sites have been converted to grassland (State 4). Others have been subject to repeated, high-graded timber harvest coupled with domestic livestock grazing (State 5). Fire suppression has resulted in increased canopy density, which has affected the abundance and diversity of ground flora. Many former reference sites have been managed effectively for timber harvest, resulting in either even-age (State 2) or uneven-age (State 3) woodlands.
Submodel
Description
Thinning can increase overall tree vigor and improve understory diversity. These woodlands tend to be rather dense, with a sparse understory and ground flora. Thinning can increase overall tree vigor and improve understory diversity. However, in the absence of fire, the diversity and cover of the ground flora is still diminished. Continual timber management, depending on the practices used, will either maintain this state, or convert the site to uneven-age (State 3) woodlands.
Submodel
Description
Composition is altered from the reference state depending on tree selection during harvest. In addition, without a regular 15 to 20 year harvest re-entry into these stands, they will slowly increase in more shade tolerant species and white oak will become less dominant and scarlet oak is often more abundant than historically. Without periodic disturbance, stem density and fire intolerant species, like hickory, increase in abundance.
Submodel
Description
Conversion of woodlands to non-native cool season grassland species such as tall fescue has been common. Steep slopes, low available water, abundant surface fragments, low organic matter contents and soil acidity make non-native grasslands difficult to maintain in a healthy, productive state on this ecological site. Occasionally, these pastures will have scattered patches of tall, mature pine. If grazing and pasture management is discontinued, oak sprouts will occur and the site will eventually transition to State 2. Forest stand improvement and tree planting practices can hasten this process.
Submodel
Description
Timbered sites subjected to repeated, high-graded timber harvests and domestic grazing transition to this state. This state exhibits an over-abundance of hickory and other less desirable tree species, and weedy understory species such as coralberry, gooseberry, poison ivy and Virginia creeper. The vegetation offers little nutritional value for cattle, and excessive stocking damages tree boles, degrades understory species composition and results in soil compaction and accelerated erosion and runoff. Exclusion of cattle from sites in this state coupled with uneven-age management techniques will cause a transition to State 3 (Uneven-Age).
Submodel
Mechanism
This transition typically results from even-age timber management practices, such as clear-cut, seed tree or shelterwood harvest.
Mechanism
This transition typically results from uneven-age forest management practices, such as single tree or group selection harvest and fire suppression.
Mechanism
This transition is the result of clearing the woodland community and planting pasture species. Soil erosion can be extensive in this process, along with loss of organic matter. Liming and fertilizing associated with pasture management typically raises the soil pH and increases the cation concentration (such as calcium and magnesium) of the upper soil horizons.
Mechanism
Forest stand improvement; prescribed fire; extended rotations
Mechanism
This transition typically results from uneven-age forest management practices.
Mechanism
Forest stand improvement; prescribed fire; extended rotations
Mechanism
This transition typically results from even-age forest management practices, such as clear-cut, seed tree or shelterwood harvest.
Mechanism
This transition typically results from tree planting; long-term succession; no grazing
.
Mechanism
This transition results from the cessation of cattle grazing and associated pasture management such as mowing and brush-hogging. Herbicide application, tree planting and timber stand improvement techniques can speed up this otherwise very lengthy transition.
Mechanism
Uneven-age management; no grazing; forest stand improvement
Model keys
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The Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.