Creek Bottomland
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
-
Transition T1A
Invasion by Chinese tallow
More details -
Transition T1B
Clearcut, site preparation, tree planting
More details -
Transition T1C
Clearcut, grass/crop planting
More details -
Restoration pathway R2A
Removal of Chinese tallow, return over/understory to natives
More details -
Transition T2A
Clearcut, site preparation, tree planting
More details -
Transition T2B
Clearcut, grass/crop planting
More details -
Restoration pathway R3A
Tree planting, return flooding intervals
More details -
Transition T3A
Clearcut, abandonment, Chinese tallow invasion
More details -
Transition T3B
Clearcut, grass/crop planting
More details -
Restoration pathway R4A
Tree planting, return flooding intervals
More details -
Transition T4A
Oldfield abandonment, Chinese tallow invasion
More details -
Transition T4B
Clearcut, site preparation, tree planting
More details -
No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
Two communities exist in the Forest State: the Water Oak/White Oak Forest Community (1.1) and the Stream Bank Community (1.2). The overall state has a high overstory canopy cover (75 to 95 percent) of hardwood species with some pine mixed in. Basal areas usually range from 80 to 100 square feet per acre, but can be as low as 60 and as high as 140 square feet per acre. The dominant overstory species are water oak, white oak, sweetgum (Liquidambar styracifllua), and loblolly pine. Flooding in State 1 is common varying from brief to very brief durations depending on micro-relief, amount of precipitation, and current saturation of the soil. Flooding can occur anytime, but typically occurs during the dormant-growing season (October to February).
Submodel
Description
Chinese tallow (Triadica sebifera) is an undesired, invasive species brought to the United States in 1776 (Randall & Marinelli, 1996). Rapid expansion along the gulf coastal states has allowed the species to invade many ecosystems and consequently reduce diversity. Tallow trees are known to cause gastrointestinal upset, contact dermatitis, and toxicity in livestock and humans. Mechanical and chemicals options exist as a means to control the trees.
Submodel
Description
The Plantation State is a result of conversion activities. The landowner has maximized silviculture production by planting a monoculture of tree species.
Submodel
Mechanism
The transition from the State 1 to State 2 is a result of occupancy by Chinese tallow. Chinese tallow invades oftentimes from upstream as their seeds are carried by floodwaters. Tallow trees grow and spread quickly throughout infected sites.
Mechanism
The transition is because of the land manager maximizing silviculture potential. Merchantable timber is harvested by clearcut, then the site is prepared and planted to a monoculture of trees.
Mechanism
The transition is because of the land manager converting to agricultural production. Merchantable timber is harvested by clearcut, then the site is prepared and planted to either a planted grass for grazing livestock or row crops for food and fiber.
Mechanism
The driver for restoration is control of Chinese tallow. Although an option, mechanical removal of the trees is difficult because they readily regrow from roots and seeds. Several chemicals methods are available including glyphosate for cut-stump treatments, triclopyr for cut-stump and foliar treatments, imazamox for broad spectrum application, and imazapyr as a foliar spray. Many aquatic herbicides have water use restrictions and can potentially kill hardwoods, so labels and restrictions should be read carefully prior to application.
Mechanism
The transition is because of the land manager maximizing silviculture potential. Merchantable timber is harvested by clearcut, then the site is prepared and planted to a monoculture of trees.
Mechanism
The transition is because of the land manager converting to agricultural production. Merchantable timber is harvested by clearcut, then the site is prepared and planted to either a planted grass for grazing livestock or row crops for food and fiber.
Mechanism
This restoration pathway may be accomplished by removing planted trees (pine or other hardwood) and replanting bottomland hardwoods. Restoration efforts for bottomland hardwood forests have proven difficult and much research has been done on these ecosystems. Many times restoring the function of the ecosystem is the most difficult obstacle. Evapotranspiration and hyrdoperiod are closely linked and may never fully be restored until a forested condition exists again (Stanturf et al., 2001).
Local tree availability may limit the possibilities of species composition. Careful planning of available species, site design, and further management actions should be conversed with a knowledgeable restoration source. With this in mind, oftentimes late summer and early fall are the best times to begin because of possibly wet conditions during the late fall to early spring. Many detailed guides have been written to assist with restoration, and suggested readings include, “A Guide to Bottomland Hardwood Restoration” (Allen et al., 2001).
Mechanism
This community transition is caused by neglecting the plantation understory. Without control, the understory becomes a dense thicket and can be invaded by Chinese tallow.
Mechanism
The transition is because of the land manager maximizing agricultural production. Merchantable timber is harvested by clearcut, then the site is prepared and planted to either an improved grass or row crops.
Mechanism
This restoration pathway may be accomplished by restoring bottomland hardwoods. Restoration efforts for bottomland hardwood forests have proven difficult and much research has been done on these ecosystems. Many times restoring the function of the ecosystem is the most difficult obstacle. Evapotranspiration and hyrdoperiod are closely linked and may never fully be restored until a forested condition exists again (Stanturf et al., 2001).
Local tree availability may limit the possibilities of species composition. Careful planning of available species, site design, and further management actions should be conversed with a knowledgeable restoration source. With this in mind, oftentimes late summer and early fall are the best times to begin because of possibly wet conditions during the late fall to early spring. Many detailed guides have been written to assist with restoration, and suggested readings include, “A Guide to Bottomland Hardwood Restoration” (Allen et al., 2001).
Mechanism
This community transition is caused by neglecting the pasture or not replanting crops. Without control, the understory becomes a dense thicket and can be invaded by Chinese Tallow.
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.