Natural Resources
Conservation Service
Mesic Temperature Regime, High Terraces, Very Rare Inundation
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
-
Transition T1A
Clearcut logging or other large-scale disturbances that cause canopy removal.
More details -
Transition T1B
Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs.
More details -
Transition T1C
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, and planting of crop or cover crop seed.
More details -
Transition T2A
Long-term natural succession.
More details -
Transition T2B
Site preparation and tree planting.
More details -
Transition T2C
Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs.
More details -
Transition T2D
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, weed control, planting of crop or cover crop seed.
More details -
Transition T3A
Abandonment of forestry practices.
More details -
Transition T3B
Timber harvest, mechanical stump and debris removal, seedbed preparation, and planting of perennial grasses and forbs.
More details -
Transition T3C
Timber harvest, mechanical stump and debris removal, seedbed preparation, fertilizer/lime, weed control, planting of crop or cover crop seed.
More details -
Transition T4A
Long-term cessation of grazing.
More details -
Transition T4B
Site prep and tree planting.
More details -
Transition T4C
Seedbed preparation, applications of fertilizer/lime, weed control, and planting of crop or cover crop seed.
More details -
Transition T5A
Agricultural abandonment.
More details -
Transition T5B
Site preparation and tree planting.
More details -
Transition T5C
Seedbed preparation, weed control, and planting of perennial grasses and forbs.
More details -
No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
This mature forest state supports a closed canopy forest dominated by a diverse mixture of mesophytic upland species and bottomland hardwoods.
Characteristics and indicators
Stands are uneven-aged with at least some old trees present. In contrast with young, recently disturbed stands, native species are more likely to dominate the shrub and herb layers. The subcanopy layer is usually well-developed, featuring a diverse group of tree species.
Dominant plant species
willow oak (Quercus phellos), tree
white oak (Quercus alba), tree
American beech (Fagus grandifolia), tree
northern red oak (Quercus rubra), tree
American elm (Ulmus americana), tree
red maple (Acer rubrum), tree
winged elm (Ulmus alata), tree
sweetgum (Liquidambar styraciflua), tree
bitternut hickory (Carya cordiformis), tree
American holly (Ilex opaca), tree
blackhaw (Viburnum prunifolium), shrub
bursting-heart (Euonymus americanus), shrub
American holly (Ilex opaca), shrub
Virginia creeper (Parthenocissus quinquefolia), shrub
possumhaw (Ilex decidua), shrub
crossvine (Bignonia capreolata), shrub
greenbrier (Smilax), shrub
eastern poison ivy (Toxicodendron radicans), shrub
southern arrowwood (Viburnum recognitum), shrub
white edge sedge (Carex debilis), grass
eastern star sedge (Carex radiata), grass
eastern narrowleaf sedge (Carex amphibola), grass
Indian woodoats (Chasmanthium latifolium), grass
variable panicgrass (Dichanthelium commutatum), grass
Bosc's panicgrass (Dichanthelium boscii), grass
cypress panicgrass (Dichanthelium dichotomum), grass
early bluegrass (Poa cuspidata), grass
autumn bluegrass (Poa autumnalis), grass
nodding fescue (Festuca subverticillata), grass
Christmas fern (Polystichum acrostichoides), grass
white avens (Geum canadense), grass
partridgeberry (Mitchella repens), grass
littlebrownjug (Hexastylis arifolia), grass
Canadian blacksnakeroot (Sanicula canadensis), grass
smooth Solomon's seal (Polygonatum biflorum), grass
helmet flower (Scutellaria integrifolia), grass
licorice bedstraw (Galium circaezans), grass
Canadian wildginger (Asarum canadense), grass
jumpseed (Polygonum virginianum), grass
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 usually even.
Submodel
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).
Dominant plant species
loblolly pine (Pinus taeda), tree
sweetgum (Liquidambar styraciflua), tree
red maple (Acer rubrum), tree
blackgum (Nyssa sylvatica), tree
Virginia pine (Pinus virginiana), tree
oak (Quercus), tree
hybrid hickory (Carya), tree
grape (Vitis), shrub
Japanese honeysuckle (Lonicera japonica), shrub
greenbrier (Smilax), shrub
St. Johnswort (Hypericum), shrub
rosette grass (Dichanthelium), grass
oatgrass (Danthonia), grass
sedge (Carex), grass
Christmas fern (Polystichum acrostichoides), grass
fan clubmoss (Lycopodium digitatum), grass
ebony spleenwort (Asplenium platyneuron), grass
partridgeberry (Mitchella repens), grass
cinquefoil (Potentilla), grass
Submodel
Description
This converted state is dominated by herbaceous forage species.
Resilience management
Flooding:
This ecological site is subject to flooding in some years during periods of unusually wet weather. The duration of flooding is usually short-lived, though pastures may remain wet for longer periods. Landowners will need access to additional pasture or housing that is not subject to flooding, on which to move livestock as needed.
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.), curly dock (Rumex crispus), bitter dock (Rumex obtusifolius), Virginia buttonweed (Diodia virginiana), Oriental lady's thumb (Polygonum cespitosum var. longisetum), Carolina horsenettle (Solanum carolinense), small carpetgrass (Arthraxon hispidus), nimblewill (Muhlenbergia schreberi), Nepalese browntop (Microstegium vimineum), and common rush (Juncus effusus), among others. 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 Chinese privet (Ligustrum sinense), blackberry (Rubus spp.), rose (Rosa spp.), and common persimmon (Diospyros virginiana).
Dominant plant species
tall fescue (Schedonorus arundinaceus), grass
orchardgrass (Dactylis glomerata), grass
dallisgrass (Paspalum dilatatum), grass
Johnsongrass (Sorghum halepense), grass
perennial ryegrass (Lolium perenne), grass
Kentucky bluegrass (Poa pratensis), grass
beaked panicgrass (Panicum anceps), grass
broomsedge bluestem (Andropogon virginicus), grass
nimblewill (Muhlenbergia schreberi), grass
Nepalese browntop (Microstegium vimineum), grass
white clover (Trifolium repens), grass
red clover (Trifolium pratense), grass
vetch (Vicia), grass
narrowleaf plantain (Plantago lanceolata), grass
dogfennel (Eupatorium capillifolium), grass
Submodel
Transition T1A
Clearcut logging or other large-scale disturbances that cause canopy removal.
Mechanism
The reference state can transition to the secondary succession state through clearcut logging or other large-scale disturbances that cause canopy removal.
Transition T1B
Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs.
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.
Transition T1C
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, and planting of crop or cover crop seed.
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.
Constraints to recovery
Even with long-term natural succession, non-native species that gain a foothold after disturbance may still be problematic in the understory of bottomland forests nearing maturity. It is unknown whether the understory will eventually approach the composition of old-growth stands without significant human intervention. Species such as Chinese privet (Ligustrum sinense) and Nepalese browntop (Microstegium vimineum) may become fixtures in mature bottomland forests of the near future, due to their reproductive capacity and tolerance for shade. The importance of these weedy invaders will likely decline over time, though the extent to which they will persist in the long-term absence of anthropogenic disturbance is unknown.
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.
Transition T2C
Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs.
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.
Transition T2D
Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, weed control, planting of crop or cover crop seed.
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 managed pine plantation state can transition to the secondary succession state through abandonment of forestry practices (with or without timber tree harvest).
Transition T3B
Timber harvest, mechanical stump and debris removal, seedbed preparation, and planting of perennial grasses and forbs.
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.
Transition T3C
Timber harvest, mechanical stump and debris removal, seedbed preparation, fertilizer/lime, weed control, planting of crop or cover crop seed.
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.
Transition T4C
Seedbed preparation, applications of fertilizer/lime, weed control, and planting of crop or cover crop seed.
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.
Transition T5C
Seedbed preparation, weed control, and planting of perennial grasses and forbs.
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.
Model keys
Briefcase
Add { ecological sites } and { Major Land Resource Areas } to your briefcase by clicking on the briefcase
(
) icon wherever it occurs. Drag and drop items to reorder. Cookies are used to store briefcase items between browsing sessions. Because of this, the number of items that can be added to your briefcase is limited, and briefcase items added on one device and browser cannot be accessed from another device or browser. Users who do not wish to place cookies on their devices should not use the briefcase tool. Briefcase cookies serve no other purpose than described here and are deleted whenever browsing history is cleared.
Ecological sites
Major Land Resource Areas
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.
Accessibility statement