Loamy Floodplain Forest
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
- Transition T1A More details
- Transition T1B More details
- Transition T1C More details
- Transition T2A More details
- Transition T2B More details
- Restoration pathway R2A More details
- Transition T3A More details
- Transition T3B More details
- Restoration pathway R3A More details
- Transition T4A More details
- Transition T4B More details
- Restoration pathway R4A More details
- Transition T5A More details
- Transition T5B More details
- Transition T5C More details
-
No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
The reference plant community is categorized as an oak bottomland forest community, dominated by upland and hydrophytic oaks and herbaceous vegetation. The two community phases within the reference state are dependent on a regular flood regime. The amount and duration of flooding alters species composition, cover, and extent. Periodic pest outbreaks and wind storms have more localized impacts in the reference phases, but do contribute to overall species composition, diversity, cover, and productivity.
Submodel
Description
Agricultural tile drainage, stream channelization, and levee construction in hydrologically-connected waters have drastically changed the natural hydrologic regime of Loamy Floodplain Forests. In addition, increased amounts of precipitation and intensity have amplified flooding events (Pryor et al. 2014). This has resulted in a type conversion from the species-rich forest to a ruderal floodplain forest state. In addition, exotic species have encroached and continuously spread, reducing native diversity and ecosystem stability (Eggers and Reed 2015).
Submodel
Description
The forage state occurs when the site is converted to a farming operation that emphasizes domestic livestock production known as grassland agriculture. Fire suppression, periodic cultural treatments (e.g., clipping, drainage, soil amendment applications, planting new species and/or cultivars, mechanical harvesting) and grazing by domesticated livestock transition and maintain this state (USDA-NRCS 2003). Early settlers seeded non-native species, such as smooth brome (Bromus inermis Leyss.) and Kentucky bluegrass (Poa pratensis L.), to help extend the grazing season (Smith 1998). Over time, as lands were continuously harvested or grazed by herds of cattle, the non-native species were able to spread and expand across the landscape, reducing the native species diversity and ecological function. This state is most common on the steeply sloping sites.
Submodel
Description
The low topographic relief across the MLRA has resulted in nearly the entire area being converted to agriculture (Eilers and Roosa 1994). The continuous use of tillage, row-crop planting, and chemicals (i.e., herbicides, fertilizers, etc.) has effectively eliminated the reference community and many of its natural ecological functions in favor of crop production. Corn and soybeans are the dominant crops for the site, and oats (Avena L.) and alfalfa (Medicago sativa L.) may be rotated periodically. These areas are likely to remain in crop production for the foreseeable future. This state is most common on the gently sloping sites.
Submodel
Description
The combination of natural and anthropogenic disturbances occurring today has resulted in numerous ecosystem health issues, and restoration back to the historic reference state may not be possible. Many natural forest communities are being stressed by non-native diseases and pests, habitat fragmentation, permanent changes in hydrologic regimes, and overabundant deer populations on top of naturally-occurring disturbances (severe weather and native pests) (Flickinger 2010). However, these habitats provide multiple ecosystem services including carbon sequestration; clean air and water; soil conservation; biodiversity support; wildlife habitat; as well as a variety of cultural activities (e.g., hiking, hunting) (Millennium Ecosystem Assessment 2005; Flickinger 2010). Therefore, conservation of floodplain forests should still be pursued. Habitat reconstructions are an important tool for repairing natural ecological functioning and providing habitat protection for numerous species of Loamy Floodplain Forests. Therefore, ecological restoration should aim to aid the recovery of degraded, damaged, or destroyed ecosystems. A successful restoration will have the ability to structurally and functionally sustain itself, demonstrate resilience to the ranges of stress and disturbance, and create and maintain positive biotic and abiotic interactions (SER 2002). The reconstructed forest state is the result of a long-term commitment involving a multi-step, adaptive management process.
Submodel
Mechanism
Altered hydrology throughout the watershed transitions the site to the hydrologically-altered state (2).
Mechanism
Woody species removal and cultural treatments to enhance forage quality and yield transition the site to the forage state (3).
Mechanism
Woody species removal, tillage, seeding of agricultural crops, and non-selective herbicide transition the site to the cropland state (4).
Mechanism
Woody species removal and cultural treatments to enhance forage quality and yield transition the site to the forage state (3).
Mechanism
Woody species removal, tillage, seeding of agricultural crops, and non-selective herbicide transition the site to the cropland state (4).
Mechanism
Site preparation, tree planting, timber stand improvement, non-native species control, and water control structures installed to improve and regulate hydrology transition this site to the reconstructed forest state (5).
Mechanism
Land abandonment transitions the site to the hydrologically-altered state (2).
Mechanism
Tillage, seeding of agricultural crops, and non-selective herbicide transition this site to the cropland state (4).
Mechanism
Site preparation, tree planting, timber stand improvement, non-native species control, and water control structures installed to improve and regulate hydrology transition this site to the reconstructed forest state (5).
Mechanism
Land abandonment transitions the site to the hydrologically-altered state (2).
Mechanism
Cultural treatments to enhance forage quality and yield transitions the site to the forage state (3).
Mechanism
Site preparation, tree planting, timber stand improvement, non-native species control, and water control structures installed to improve and regulate hydrology transition this site to the reconstructed forest state (5).
Mechanism
Removal of water control structures and unmanaged invasive species populations transition this site to the hydrologically-altered state (2).
Mechanism
Tree removal and cultural treatments to enhance forage quality and yield transition the site to the forage state (3).
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.