Wet Bedrock Prairie
Scenario model
Current ecosystem state
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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
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
The reference plant community is categorized as a wet meadow community, dominated by hydrophytic vegetation. The two community phases within the reference state are dependent on periodic fires. The intensity and frequency alter species composition, cover, and extent, while regular fire intervals keep woody species from encroaching. Drought and herbivory have more localized impacts in the reference phases, but do contribute to overall species composition, diversity, cover, and productivity.
Submodel
Description
Hydrology is the most important determinant of wetlands and wetland processes. Hydrology modifies and determines the physiochemical environment (i.e., sediments, soil chemistry, water chemistry) which in turn directly affects the vegetation, animals, and microbes (Mitsch and Gosselink 2007). Human activities on landscape hydrology have greatly altered Wet Bedrock Prairies. Alterations such as agricultural tile draining and conversion to cropland on adjacent lands have changed the natural hydroperiod and rate of sedimentation as well as increased nutrient pollution (Werner and Zedler 2003; Mitsch and Gosselink 2007; Eggers and Reed 2015).
Submodel
Description
The forage state occurs when the reference state 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.
Submodel
Description
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.
Submodel
Description
Wet meadow habitats provide multiple ecosystem services including flood abatement, water quality improvement, and biodiversity support. However, many wet meadow communities have been stressed from watershed-scale changes in hydrology or eliminated as a result of type conversions to agricultural production, thereby significantly reducing these services (Zedler 2003). The extensive alterations of lands adjacent to Wet Bedrock Prairies may not allow for restoration back to the historic reference condition. However, ecological reconstruction can aim to aid the recovery of degraded, damaged or destroyed functions. A successful reconstruction will have the ability to structurally and functionally sustain itself, demonstrate resilience to the natural ranges of stress and disturbance, and create and maintain positive biotic and abiotic interactions (SER 2002; Mitsch and Jørgensen 2004).
Submodel
Mechanism
Direct and indirect alterations to the landscape hydrology from human-induced land development transition the site to the hydrologically-altered state (2).
Mechanism
Cultural treatments to enhance forage quality and yield transitions this site to the forage state (3).
Mechanism
Installation of drain tiles, tillage, seeding of agricultural crops, and non-selective herbicide transition the site to the cropland state (4).
Mechanism
Cultural treatments to enhance forage quality and yield transition the site to the forage state (3).
Mechanism
Installation of drain tiles, tillage, seeding of agricultural crops, and non-selective herbicide transition the site to the cropland state (4).
Mechanism
Hydroperiod restoration, site preparation, non-native species control, and seeding native species transition the site to the reconstructed wet meadow state (5).
Mechanism
Land abandonment and natural succession by opportunistic species transition 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, invasive species control, and seeding native species transition this site to the reconstructed wet meadow state (5).
Mechanism
Land abandonment and natural succession by opportunistic species transition 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, invasive species control, and seeding native species transition this site to the reconstructed sedge meadow state (5).
Mechanism
Land is abandoned and left fallow; natural succession by opportunistic species transition this site the hydrologically-altered state (2).
Mechanism
Cultural treatments to enhance forage quality and yield transition the site to the forage state (3).
Model keys
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