Deep Loess Upland Woodland
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Fire suppression; even-age management
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Transition T1B
Fire suppression; uneven age management
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Transition T1C
Disturbances; logging; unmanaged grazing
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Restoration pathway R1A
Restoration; prescribed fire
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Transition T2A
Uneven age management
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Transition R1B
Restoration; prescribed fire
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Transition T3A
Even-age management
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Transition T4A
Plantings; prescribed grazing
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Transition T5C
Livestock exclusion; tree planting; forest stand improvement.
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Transition T5A
Tillage; cropping system
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Transition T5B
Light grazing; high-grade harvesting
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Transition T6B
Uneven-age management; tree planting; forest stand improvement
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Transition T6C
Tillage; crop production
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Transition T6A
Pasture establishment and management
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
The historical reference state for this ecological site was old growth oak woodland. The woodland was dominated by white oak and black oak. Maximum tree age was likely 150 to 300 years. Periodic disturbances from fire, wind or ice as well as grazing by native large herbivores 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. Reference states are very rare today. Fire suppression has resulted in increased canopy density, which has affected the abundance and diversity of ground flora. Most, if not all, reference states are currently altered because of fire suppression, timber harvesting, domestic grazing or clearing and conversion to grassland or cropland.
Submodel
Description
An even-age managed forest can resemble the reference state. The primary difference is tree age, most being only 50 to 90 years old. Composition is also likely altered from the reference state depending on tree selection during harvests and disturbance activities. Without a regular 15 to 20 year harvest re-entry into these stands, they will slowly increase in more shade tolerant species such as sugar maple and white oak will become less dominant.
This state can be restored to a reference state by modifying or eliminating timber harvests, extending rotations, incorporating selective thinning, and re-introducing prescribed fire.
Submodel
Description
Due to selective single tree harvesting canopy densities have increased. Composition is likely altered from the Reference State depending on tree selection during harvest. This state will slowly increase in more shade tolerant species and white oak will become less dominant and is also dense because of fire suppression. Without periodic canopy disturbance, stem density and fire intolerant species, like hickory and maple will increase in abundance.
This state can be restored to a reference state by modifying or eliminating timber harvests, extending rotations, incorporating selective thinning, and re-introducing prescribed fire.
Submodel
Description
This is a state that exists currently with intensive cropping of corn, soybeans, and wheat, especially on slopes of 5 percent or less. Some conversion to cool season grassland occurs for a limited period of time before transitioning back to cropland. Limited acres are sometimes converted to native warm season grassland.
Submodel
Description
Conversion of other states to non-native cool season species such as tall fescue, orchard grass, and red clover has been common. Occasionally, these pastures will have scattered oaks. Long term uncontrolled grazing can cause significant soil erosion and compaction. A return to the reference state may be impossible, requiring a very long term series of management options.
Two community phases are recognized in the grassland state, with shifts between phases based on types of management. Poor management will result in a shift to Community 5.2 that shows an increase in oak sprouting and increases in broomsedge densities. If oak sprouting is left unchecked and grazing is eliminated or reduced then over time this state will transition to an even-age managed woodland (livestock controlled and woodland management initiated) or to a high-graded/grazed woodland (continued grazing, high graded harvesting, and no woodland management).
Submodel
Description
States that were subjected to repeated, high-grading timber harvests and uncontrolled domestic grazing will transition to a High-Graded/Grazed Woodland 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 existing vegetation offers little nutritional value for cattle, and excessive cattle stocking damages tree boles, degrades understory species composition and results in soil compaction and accelerated erosion and runoff.
Two common transitions from this state are woody clearing and conversion to State 5, Grassland or removing livestock, limited harvesting, and allowing long term succession to occur to some other woodland or forest state.
Submodel
Mechanism
This transition is the result of fire suppression and even-aged management.
Mechanism
This transition is the result of fire suppression and uneven-aged management.
Mechanism
This transition is the result of poorly planned harvests and uncontrolled livestock grazing.
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Mechanism
This restoration pathway is the result of prescribed fire and extended rotations.
Mechanism
This transition is the result of uneven-age management and thinning.
Mechanism
This restoration pathway is the result of prescribed fire and extended rotations.
Mechanism
This transition is the result of even-age management and thinning.
Mechanism
This transition is the result of grassland planting, grassland management and prescribed grazing.
Mechanism
This transition is the result of livestock exclusion, tree planting, extended rotations, and forest stand improvement.
Mechanism
This transition is the result of tillage and conservation cropping system.
Mechanism
This transition is the result of light grazing, woody regrowth, and high-grade harvesting.
Mechanism
This transition is the result of uneven-age management, tree planting, cessation of grazing, forest stand improvement, and extended rotations.
Mechanism
This transition is the result of clearing, tillage and crop rotation.
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.