Mesic Temperature Regime, Basic Upland Forest, Moist
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Clearcut logging or other large-scale disturbances that cause canopy removal.
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Transition T1B
Selective removals of the most valuable timber specimens, leaving inferior trees behind.
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Transition T1C
Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs.
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Transition T1D
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, and planting of crop or cover crop seed.
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Transition T2A
Long-term natural succession.
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Transition T2B
Site preparation and tree planting.
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Transition T2C
Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs.
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Transition T2D
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, weed control, planting of crop or cover crop seed.
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Transition T3A
Clearcut logging or other large-scale disturbances that cause canopy removal.
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Transition T3C
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, weed control, and planting of perennial grasses and forbs.
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Transition T3D
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, weed control, planting of crop or cover crop seed.
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Transition T4A
Abandonment of forestry practices.
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Transition T4B
Timber harvest, mechanical stump and debris removal, seedbed preparation, and planting of perennial grasses and forbs.
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Transition T4C
Timber harvest, mechanical stump and debris removal, seedbed preparation, fertilizer/lime, weed control, planting of crop or cover crop seed.
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Transition T5A
Long-term cessation of grazing.
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Transition T5B
Site preparation and tree planting.
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Transition T5C
Seedbed preparation, applications of fertilizer/lime, weed control, and planting of crop or cover crop seed.
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Transition T6A
Agricultural abandonment.
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Transition T6B
Site preparation and tree planting.
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Transition T6C
Seedbed preparation, weed control, and planting of perennial grasses and forbs.
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
This mature forest state is generally dominated by mesophytic and dry-mesophytic oaks. It usually has a greater proportion of hickories, elms, and ashes than acidic oak-hickory forest types.
Characteristics and indicators
Stands are uneven-aged with at least some old trees present. Pines make up a minority of the canopy cover.
Resilience management
Deer population management is critical to sustaining the diversity of herbaceous understory species.
Submodel
Description
This state develops in the immediate aftermath of agricultural abandonment, clearcut logging, or other large-scale disturbances that lead to canopy removal. Which species colonize a particular location in the wake of a disturbance does involve a considerable degree of chance. It also depends a great deal on the type, duration, and magnitude of the disturbance event.
Characteristics and indicators
Plant age distribution is even. Plants exhibit pioneering traits such as rapid growth, early reproduction, and shade-intolerance.
Submodel
Description
This state develops as a consequence of high-grading, where the most valuable trees are removed, leaving less desirable timber specimens behind. Trees left behind include undesirable timber species, trees of poor form, diseased trees, or genetically inferior trees.
Characteristics and indicators
Typically, high-graded stands consist of a combination of residual stems from the previous stand, a high proportion of undesirable shade-tolerant species, along with some regrowth from desirable timber species. In some cases, large-diameter trees of desirable timber species may be present, but upon closer inspection, these trees usually have serious defects that resulted in their being left behind in earlier cuts.
Resilience management
Landowners with high-graded stands have two options for improving timber production: 1) rehabilitate, or 2) regenerate. To rehabilitate a stand, the landowner must evaluate existing trees to determine if rehabilitation is justified. If the proportion of high-quality specimens present in the stand is low, then the stand should be regenerated. In many cases, poor quality of the existing stand is the result of decades of mismanagement. Drastic measures are often required to get the stand back into good timber production.
Description
This converted state is dominated by planted timber trees. Loblolly pine (Pinus taeda) is the most commonly planted species, though Virginia pine (Pinus virginiana) can also be successfully managed for timber in this part of the MLRA. Even-aged management is the most common timber management system.
Note: if the user wishes to convert stands dominated by hardwoods to planted pine, clearcutting will usually be necessary first, allowing herbaceous pioneers to establish on the site in the weeks or months prior to planting. Users should utilize measures described in transition T2B under these circumstances.
Resilience management
Hardwood Encroachment:
Hardwood encroachment can be problematic in managed pine plantations. Good site preparation, proper stocking, and periodic thinning are advisable to reduce hardwood competition.
Overstocking:
The overstocked condition commonly occurs in naturally regenerated stands. When competition from other pines begins to impact the health and productivity of the stand, precommercial thinning should be considered. At this point, the benefit of thinning usually outweighs the potential for invasion and competition from non-pine species. As the target window for thinning passes, the condition of the stand can slowly deteriorate if no action is taken. Under long-term overstocked conditions, trees are more prone to stresses, including pine bark beetle infestation and damage from wind or ice.
High-grading:
In subsequent commercial thinnings, care should be taken in tree selection. High quality specimens should be left to reach maturity, while slower growing trees or those with defects should be removed sooner. If high quality specimens are harvested first, trees left behind are often structurally unsound, diseased, genetically inferior, or of poor form. This can have long-term implications for tree genetics and for the condition of the stand (Felix III 1983; Miller et al. 1995, 2003; Megalos 2019).
Description
This converted state is dominated by herbaceous forage species.
Resilience management
Overgrazing and High Foot Traffic:
In areas that are subject to high foot traffic from livestock and equipment, and/or long-term overgrazing, unpalatable weedy species tend to invade, as most desirable forage species are less competitive under these conditions. High risk areas include locations where livestock congregate for water, shade, or feed, and in travel lanes, gates, and other areas of heavy use. Plant species that are indicative of overgrazing or excessive foot traffic on this ecological site include buttercup (Ranunculus spp.), plantain (Plantago spp.), curly dock (Rumex crispus), sneezeweed (Helenium amarum), cudweed (Pseudognaphalium spp.), slender yellow woodsorrel (Oxalis dillenii), Carolina horsenettle (Solanum carolinense), Virginia pepperweed (Lepidium virginicum), black medick (Medicago lupulina), Japanese clover (Kummerowia striata), annual bluegrass (Poa annua), poverty rush (Juncus tenuis), rattail fescue (Vulpia myuros), and Indian goosegrass (Eleusine indica), among others. A handful of desirable forage species are also tolerant of heavy grazing and high foot traffic, including white clover (Trifolium repens), dallisgrass (Paspalum dilatatum), and bermudagrass (Cynodon dactylon). An overabundance of these species, along with poor plant vigor and areas of bare soil, may imply that excessive foot traffic and/or overgrazing is a concern, either in the present or in the recent past.
Brush Encroachment:
Brush encroachment can be problematic in some pastures, particularly near fence lines where there is often a ready seed source. Pastures subject to low stocking density and long-duration grazing rotations can also be susceptible to encroachment from woody plants. Shorter grazing rotations of higher stocking density can help alleviate pressure from shrubs and vines with low palatability or thorny stems. Clipping behind grazing rotations, annual brush hogging, and multispecies grazing systems (cattle with or followed by goats) can also be helpful. Common woody invaders of pasture on this ecological site include rose (Rosa spp.), blackberry (Rubus spp.), saw greenbrier (Smilax bona-nox), Japanese honeysuckle (Lonicera japonica), common persimmon (Diospyros virginiana), eastern redcedar (Juniperus virginiana), black cherry (Prunus serotina), and Chinese privet (Ligustrum sinense).
Mechanism
The reference state can transition to the secondary succession state through clearcut logging or other large-scale disturbances that cause canopy removal.
Mechanism
The reference state can transition to the high-graded hardwood forest state through selective removal of the most valuable trees, leaving undesirable timber specimens behind. This may occur through multiple cutting cycles over the course of decades or longer, each cut progressively worsening the condition of the stand.
Mechanism
The reference state can transition to the pasture/hayland state through 1) mechanical tree/brush/stump/debris removal, 2) seedbed preparation, and 3) planting of perennial grasses and forbs.
Context dependence
Herbicide applications, fire, and/or root-raking can be helpful in transitioning treed land to pasture. This is done in part to limit coppicing, as many woody plants are capable of sprouting from residual plant structures left behind after clearing. Judicious use of root-raking is recommended, as this practice can have long-term repercussions with regard to soil structure. Applications of fertilizer and lime can also be helpful in establishing perennial forage species. Grazing should be deferred until grasses and forbs are well established.
Mechanism
The reference state can transition to the cropland state through 1) mechanical tree/brush/stump/debris removal, 2) seedbed preparation, 3) applications of fertilizer/lime, and 4) planting of crop or cover crop seed.
Context dependence
A broad spectrum herbicide, fire, and/or root-raking can be helpful in transitioning treed land to cropland. This is done in part to limit coppicing, as many woody plants are capable of sprouting from residual plant structures left behind after clearing. Judicious use of root-raking is recommended, as this practice can have long-term repercussions with regard to soil structure. Weedy grasses and forbs can also be problematic on these lands.
Mechanism
The secondary succession state can transition to the reference state through long-term natural succession. This process can be accelerated to some degree by a combination of prescribed burns and selective harvesting of pines and opportunistic hardwoods.
Mechanism
The secondary succession state can transition to the managed pine plantation state through site preparation and planting of timber trees. Thinning alone may be sufficient for portions of the forest if pines have already established, though it is rarely sufficient for an entire forest patch.
Mechanism
The secondary succession state can transition to the pasture/hayland state through through 1) mechanical tree/brush/stump/debris removal, 2) seedbed preparation, and 3) planting of perennial grasses and forbs.
Context dependence
A broad spectrum herbicide, fire, and/or root-raking can be helpful in transitioning wooded or semi-wooded land to pasture. This is done in part to limit coppicing, as many woody pioneers are capable of sprouting from residual plant structures left behind after clearing. Judicious use of root-raking is recommended, as this practice can have long-term repercussions with regard to soil structure. Applications of fertilizer and lime can also be helpful in establishing perennial forage species. Grazing should be deferred until grasses and forbs are well established.
Mechanism
The secondary succession state can transition to the cropland state through 1) mechanical tree/brush/stump/debris removal, 2) seedbed preparation, 3) applications of fertilizer/lime, 4) weed control, 5) planting of crop or cover crop seed.
Context dependence
A broad spectrum herbicide, fire, and/or root-raking may be needed to successfully transition land that has been fallow for some time back to cropland. This is done in part to limit coppicing, as many woody pioneers are capable of sprouting from residual plant structures left behind after clearing. Judicious use of root-raking is recommended, as this practice can have long-term repercussions with regard to soil structure. Weedy grasses and forbs can also be problematic on these lands.
Mechanism
The high-graded hardwood forest state can transition to the secondary succession state through clearcut logging or other large-scale disturbances that cause canopy removal.
Mechanism
The high-graded hardwood forest state can transition to the pasture/hayland state through 1) mechanical tree/brush/stump/debris removal, 2) seedbed preparation, and 3) planting of perennial grasses and forbs.
Context dependence
Herbicide applications, fire, and/or root-raking can be helpful in transitioning treed land to pasture. This is done in part to limit coppicing, as many woody plants are capable of sprouting from residual plant structures left behind after clearing. Judicious use of root-raking is recommended, as this practice can have long-term repercussions with regard to soil structure. Applications of fertilizer and lime can also be helpful in establishing perennial forage species. Grazing should be deferred until grasses and forbs are well established.
Mechanism
The high-graded hardwood forest state can transition to the cropland state through 1) mechanical tree/brush/stump/debris removal, 2) seedbed preparation, 3) applications of fertilizer/lime, 4) weed control, 5) planting of crop or cover crop seed.
Constraints to recovery
A broad spectrum herbicide, fire, and/or root-raking can be helpful in transitioning treed land to cropland. This is done in part to limit coppicing, as many woody pioneers are capable of sprouting from residual plant structures left behind after clearing. Judicious use of root-raking is recommended, as this practice can have long-term repercussions with regard to soil structure. Weedy grasses and forbs can also be problematic on these lands.
Mechanism
The managed pine plantation state can transition to the secondary succession state through abandonment of forestry practices (with or without timber tree harvest).
Mechanism
The managed pine plantation state can transition to the pasture/hayland state through 1) timber harvest, 2) mechanical stump and debris removal, 3) seedbed preparation, 4) planting of perennial grasses and forbs.
Context dependence
Applications of fertilizer and lime can be helpful in establishing perennial forage species. Grazing should be deferred until grasses and forbs are well established.
Mechanism
The managed pine plantation state can transition to the cropland state through 1) timber harvest, 2) mechanical stump and debris removal, 3) seedbed preparation, 4) applications of fertilizer/lime, 5) weed control, 6) planting of crop or cover crop seed.
Mechanism
The pasture/hayland state can transition to the secondary succession state through long-term cessation of grazing.
Mechanism
The pasture/hayland state can transition to the managed pine plantation state through site preparation and tree planting.
Mechanism
The pasture/hayland state can transition to the cropland state through 1) seedbed preparation, 2) applications of fertilizer/lime, 3) weed control, and 4) planting of crop or cover crop seed.
Mechanism
The cropland state can transition to the secondary succession state through agricultural abandonment.
Mechanism
The cropland state can transition to the managed pine plantation state through site preparation and tree planting.
Mechanism
The cropland state can transition to the pasture/hayland state through 1) seedbed preparation, 2) weed control, and 3) planting of perennial forage grasses and forbs.
Context dependence
To convert cropland to pasture or hayland, weed control and good seed-soil contact are important. It is also critical to review the labels of herbicides used for weed control and on the previous crop. Many herbicides have plant-back restrictions, which if not followed could carryover and kill forage seedlings as they germinate. Grazing should be deferred until grasses and forbs are well established.
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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.