Low-Base Chert Upland 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
- Transition T1D More details
- Restoration pathway R1B More details
- Transition T2A More details
- Transition T2B More details
- Restoration pathway R1A More details
- Transition T3A More details
- Transition T3B More details
- Transition T4A More details
- Transition T4B More details
- Transition T5A More details
- Transition T6B More details
- Transition T6A 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The historical reference state for this Ecological Site was old growth oak woodland.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 5). Others have been subject to repeated, high-graded timber harvest coupled with domestic livestock grazing (State 6). 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
These woodlands tend to be rather dense, with a sparse understory and ground flora. 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
Uneven-Age Managed Woodlands resemble their reference state. The biggest differences are tree age, most being only 50 to 90 years old and denser understories. Composition is also likely altered from the reference state depending on tree selection during harvest. Scarlet oak is often more abundant than historically. 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. Without periodic disturbance, stem density and fire intolerant species, like hickory, increase in abundance.
Submodel
Description
Many areas were planted to plantations of shortleaf pine from the 1940’s to the early 1960’s. They are now mature plantations that are usually a mono-culture of a dense pine overstory with a brushy understory of oak and hickory and a dense carpet of shortleaf pine needles on the ground. They lack the diversity and structure. Restoration to phase 1.2 of the reference state is a long-term prospect, requiring extensive thinning, long-term prescribed fire, and perhaps planting of native ground flora species.
Submodel
Description
Conversion of woodlands to non-native cool season grassland species such as tall fescue has been common. 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 shortleaf 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 buckbrush, 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). This state will be transitioned to a grassland state through clearing and grassland planting or to a pine plantation through clearing, tree planting and fire control.
Submodel
Mechanism
This transition typically results from even-age forest management practices, such as clear-cut, seed tree or shelterwood harvest and fire suppression.
Mechanism
This transition typically results from uneven-age forest management practices, such as clear-cut, seed tree or shelterwood 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
This transition is the result of poorly planned timber harvest techniques such as high-grading, accompanied by unmanaged livestock grazing. Soil erosion and compaction often result from cattle grazing after the understory has been damaged.
Mechanism
Restoration activities include uneven-age management; extended rotations; prescribed fire every 5-10 years
Mechanism
This transition typically results from uneven-age forest management practices, such as single tree or group selection harvest.
Mechanism
This transition is the result of the systematic application of prescribed fire. Mechanical thinning may also be used. Tree planting with shortleaf pine.
Mechanism
This restoration pathway generally requires forest management practices with extended rotations that allow mature trees to exceed ages of about 100 years. Prescribed fire is part of the restoration process. Mechanical thinning may be necessary in dense woodlands.
Mechanism
This transition typically results from even-age forest management practices, such as clear-cut, seed tree or shelterwood harvest.
Mechanism
This transition is the result of the systematic application of prescribed fire. Mechanical thinning may also be used. Shortleaf pine tree planting.
Mechanism
This transition typically results from even-age forest management practices, such as clear-cut, seed tree or shelterwood harvest and fire suppression.
Mechanism
This transition typically results from even-age forest management practices, such as single tree or group selection harvest; thinning; fire cessation.
Mechanism
This transition results from the cessation of livestock grazing and associated pasture management such as mowing and brush-hogging. Herbicide application, tree planting and forest stand improvement techniques can speed up this otherwise very lengthy transition.
Mechanism
This transition typically results from uneven-age forest management practices, such as single tree or group selection harvest. Tree planting, mechanical thinning and other forest stand improvement techniques may be helpful to decrease the transition time.
Mechanism
This transition is the result of clearing the woodland communities 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.
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.