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Ecological site F115XC010IL

Chert Exposed Backslope Woodland

Last updated: 12/30/2024
Accessed: 01/10/2025

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General information

Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.

MLRA notes

Major Land Resource Area (MLRA): 115X–Central Mississippi Valley Wooded Slopes

This MLRA is characterized by deeply dissected, loess-covered hills bordering well defined valleys of the Illinois, Mississippi, Missouri, Ohio, and Wabash Rivers and their tributaries. It is used to produce cash crops and livestock. About one-third of the area is forested, mostly on the steeper slopes. This area is in Illinois (50 percent), Missouri (36 percent), Indiana (13 percent), and Iowa (1 percent) in two separate areas. It makes up about 25,084 square miles (64,967 square kilometers).

Most of this area is in the Till Plains section and the Dissected Till Plains section of the Central Lowland province of the Interior Plains. The Springfield-Salem plateaus section of the Ozarks Plateaus province of the Interior Highlands occurs along the Missouri River and the Mississippi River south of the confluence with the Missouri River. The nearly level to very steep uplands are dissected by both large and small tributaries of the Illinois, Mississippi, Missouri, Ohio, and Wabash Rivers. The Ohio River flows along the southernmost boundary of this area in Indiana. Well defined valleys with broad flood plains and numerous stream terraces are along the major streams and rivers. The flood plains along the smaller streams are narrow. Broad summits are nearly level to undulating. Karst topography is common in some parts along the Missouri and Mississippi Rivers and their tributaries. Well-developed karst areas have hundreds of sinkholes, caves, springs, and losing streams. In the St. Louis area, many of the karst features have been obliterated by urban development.

Elevation ranges from 90 feet (20 meters) on the southernmost flood plains to 1,030 feet (320 meters) on the highest ridges. Local relief is mainly 10 to 50 feet (3 to 15 meters) but can be 50 to 150 feet (15 to 45 meters) in the steep, deeply dissected hills bordering rivers and streams. The bluffs along the major rivers are generally 200 to 350 feet (60 to 105 meters) above the valley floor.

The uplands in this MLRA are covered almost entirely with Peoria Loess. The loess can be more than 7 feet (2 meters) thick on stable summits. On the steeper slopes, it is thin or does not occur. In Illinois, the loess is underlain mostly by Illinoian-age till that commonly contains a paleosol. Pre-Illinoian-age till is in parts of this MLRA in Iowa and Missouri and to a minor extent in the western part of Illinois. Wisconsin-age outwash, alluvial deposits, and sandy eolian material are on some of the stream terraces and on dunes along the major tributaries. The loess and glacial deposits are underlain by several bedrock systems. Pennsylvanian and Mississippian bedrock are the most extensive. To a lesser extent are Silurian, Devonian, Cretaceous, and Ordovician bedrock. Karst areas have formed where limestone is near the surface, mostly in the southern part of the MLRA along the Mississippi River and some of its major tributaries. Bedrock outcrops are common on the bluffs along the Mississippi, Ohio, and Wabash Rivers and their major tributaries and at the base of some steep slopes along minor streams and drainageways.

The annual precipitation ranges from 35 to 49 inches (880 to 1,250 millimeters) with a mean of 41 inches (1,050 millimeters). The annual temperature ranges from 48 to 58 degrees F (8.6 to 14.3 degrees C) with a mean of 54 degrees F (12.3 degrees C). The freeze-free period ranges from 150 to 220 days with a mean of 195 days.

Soils The dominant soil orders are Alfisols and, to a lesser extent, Entisols and Mollisols. The soils in the area have a mesic soil temperature regime, an aquic or udic soil moisture regime, and mixed or smectitic mineralogy. They are shallow to very deep, excessively drained to poorly drained, and loamy, silty, or clayey.

The soils on uplands in this area support natural hardwoods. Oak, hickory, and sugar maple are the dominant species. Big bluestem, little bluestem, and scattered oak and eastern redcedar grow on some sites. The soils on flood plains support mixed forest vegetation, mainly American elm, eastern cottonwood, river birch, green ash, silver maple, sweetgum, American sycamore, pin oak, pecan, and willow. Sedge and grass meadows and scattered trees are on some low-lying sites. (United States Department of Agriculture, Natural Resources Conservation Service, 2022)

LRU notes

The Central Mississippi Valley Wooded Slopes, Northern part (Land Resource Unit (LRU) (115XC) encompasses the Wyaconda River Dissected Till Plains, Mississippi River Hills, and Mississippi River Alluvial Plain (Schwegman et al. 1973; Nelson 2010). It spans three states – Illinois (73 percent), Iowa (6 percent), and Missouri (21 percent) – comprising about 13,650 square miles (Figure 1). The elevation ranges from 420 feet above sea level (ASL) along the Mississippi River floodplains to 885 feet on the upland ridges. Local relief varies from 10 to 20 feet but can be as high as 50 to 100 feet along drainageways and streams and the bluffs on the major rivers reaching 250 feet above valley floors. Wisconsin-aged loess covers the uplands, while Illinoian glacial drift lies directly below. The loess and drift deposits are underlain by several bedrock systems, including the Cretaceous, Pennsylvania, Mississippian, Silurian, Devonian, and Ordovician Systems. Wisconsin outwash deposits and sandy eolian material occur along stream terraces of major tributaries (USDA-NRCS 2006).

The vegetation across the region has undergone drastic changes over time. At the end of the last glacial episode – the Wisconsinan glaciation – the evolution of vegetation began with the development of tundra habitats, followed by a phase of spruce and fir forests, and eventually spruce-pine forests. Not until approximately 9,000 years ago did the climate undergo a warming trend which prompted the development of deciduous forests dominated by oak and hickory. As the climate continued to warm and dry, prairies began to develop approximately 8,300 years ago. Another shift in climate that resulted in an increase in moisture prompted the emergence of savanna-like habitats from 8,000 to 5,000 years before present (Taft et al. 2009). During the most recent climatic shifts, forested ecosystems maintained footholds on steep valley sides and wet floodplains. Due to the physiography of the MLRA, forests were the dominant ecosystems and were affected by such natural disturbances as droughts, wind, lightning, and occasional fire (Taft et al. 2009).

Classification relationships

USFS Subregions: Central Dissected Till Plains (251C)Section; Western Mississippi River Hills (251Ce), Mississippi River and Illinois Alluvial Plains (251Cf), Eastern Mississippi River Hills (251Ci), Galesburg Dissected Till Plain (251Cj), and Wyaconda River Dissected Till Plain (251Cm) Subsections (Cleland et al. 2007)

U.S. EPA Level IV Ecoregion: Upper Mississippi River Alluvial Plain (72d), River Hills (72f), and Western Dissected Illinoian Till Plain (72i) (USEPA 2013)

National Vegetation Classification – Ecological Systems: Ozark-Ouachita Dry-Mesic Oak Forest (CES202.708) (NatureServe 2018)

National Vegetation Classification – Plant Associations: Quercus alba – Quercus rubra – Carya tomentosa/Cornus florida Acidic Forest (CEGL002067) (Nature Serve 2018)

Biophysical Settings: North-Central Interior Dry-Mesic Oak Forest and Woodland (BpS 4913100)

Illinois Natural Areas Inventory: Dry upland forest (White and Madany 1978)

Missouri Terrestrial Natural Communities: Dry chert woodland, dry-mesic chert woodland (Nelson 2010)

Ecological site concept

Chert Exposed Backslope Woodlands are located within the green areas on the map. They occur on south and west facing upland backslopes. The soils are Alfisols that are well to somewhat excessively drained and very deep, formed in residuum weathered from cherty limestone.

The historic pre-European settlement vegetation on this ecological site was dominated by a closed canopy of oaks. White oak (Quercus alba L.) and black oak (Quercus velutina Lam.) are the dominant species in the tree canopy, but shagbark hickory (Carya ovata (Mill.) K. Koch) and mockernut hickory (Carya tomentosa (Lam.) Nutt.) can also be present (NatureServe 2018). Little bluestem (Schizachyrium scoparium (Michx.) Nash) and woman’s tobacco (Antennaria plantaginifolia (L.) Richardson) are dominant herbs (Nelson 2010). Fire is the primary disturbance factor that maintains this ecological site, while storm damage and drought are secondary factors (LANDFIRE 2009).

Associated sites

F115XC005IL	Loess Upland Forest Loess and loess-covered substrates on uplands including Atlas, Baylis, Bunkum, Caseyville, Creal, Derinda, Dodge, Fayette, Fishhook, Hickory, Kendall, Keomah, Keswick, Menfro, Metea, Navlys, Rozetta, Seaton, Stookey, Stronghurst, Sylvan, Thebes, Timula, Ursa, and Winfield soils
F115XC009IL	Chert Protected Backslope Forest Parent material is residuum from cherty limestone on north and east-facing backslopes including Goss soils

F115XC005IL

Loess Upland Forest

Loess and loess-covered substrates on uplands including Atlas, Baylis, Bunkum, Caseyville, Creal, Derinda, Dodge, Fayette, Fishhook, Hickory, Kendall, Keomah, Keswick, Menfro, Metea, Navlys, Rozetta, Seaton, Stookey, Stronghurst, Sylvan, Thebes, Timula, Ursa, and Winfield soils

F115XC009IL

Chert Protected Backslope Forest

Parent material is residuum from cherty limestone on north and east-facing backslopes including Goss soils

Similar sites

F115XC008IL	Loess Exposed Backslope Woodland Loess Exposed Backslope Woodlands occur on similar landscapes and positions but parent material is loess or loess-covered substrates.

F115XC008IL

Loess Exposed Backslope Woodland

Loess Exposed Backslope Woodlands occur on similar landscapes and positions but parent material is loess or loess-covered substrates.

Table 1. Dominant plant species

Tree	(1) Quercus alba (2) Quercus velutina
Shrub	Not specified
Herbaceous	(1) Schizachyrium scoparium (2) Antennaria plantaginifolia

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Physiographic features

Chert Exposed Backslope Woodlands occur on south and west facing upland backslopes. They are situated on elevations ranging from approximately 800 to 1200 feet ASL. The site does not experience flooding but rather generates runoff to adjacent, downslope ecological sites.

Figure 1. Location of Chert Exposed Backslope Woodland ecological site within LRU 115XC.

Figure 2. Representative block diagram of Chert Exposed Backslope Woodland and associated ecological sites.

Table 2. Representative physiographic features

Hillslope profile	(1) Backslope
Slope shape across	(1) Convex
Slope shape up-down	(1) Convex
Landforms	(1) Upland
Runoff class	High
Elevation	244 – 366 m
Slope	18 – 70%
Water table depth	203 cm
Aspect	W, NW, S, SW

Climatic features

The Central Mississippi Valley Wooded Slopes, Northern Part falls into the humid subtropical (Cfa) and hot-summer humid continental climate (Dfa) Köppen-Geiger climate classifications (Peel et al. 2007). The two main factors that drive the climate of the MLRA are latitude and weather systems. Latitude, and the subsequent reflection of solar input, determines air temperatures and seasonal variations. Solar energy varies across the seasons, with summer receiving three to four times as much energy as opposed to winter. Weather systems (air masses and cyclonic storms) are responsible for daily fluctuations of weather conditions. High-pressure systems are responsible for settled weather patterns where sun and clear skies dominate. In fall, winter, and spring, the polar jet stream is responsible for the creation and movement of low-pressure systems. The clouds, winds, and precipitation associated with a low-pressure system regularly follow high-pressure systems every few days (Angel n.d.).

The soil temperature regime of LRU 115XC is classified as mesic, where the mean annual soil temperature is between 46 and 59°F (USDA-NRCS 2006). Temperature and precipitation occur along a north-south gradient, where temperature and precipitation increase the further south one travels. The average freeze-free period of this ecological site is about 190 days, while the frost-free period is about 168 days. The majority of the precipitation occurs as rainfall in the form of convective thunderstorms during the growing season. Average annual precipitation is 41 inches, which includes rainfall plus the water equivalent from snowfall. The average annual low and high temperatures are 44 and 64°F, respectively.

Table 3. Representative climatic features

Frost-free period (characteristic range)	170 days
Freeze-free period (characteristic range)	182 days
Precipitation total (characteristic range)	991-1,041 mm
Frost-free period (actual range)	170 days
Freeze-free period (actual range)	182 days
Precipitation total (actual range)	991-1,041 mm
Frost-free period (average)	170 days
Freeze-free period (average)	182 days
Precipitation total (average)	1,016 mm

Characteristic range

Actual range

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Figure 3. Monthly precipitation range

Characteristic range

Actual range

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Figure 4. Monthly minimum temperature range

Characteristic range

Actual range

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Figure 5. Monthly maximum temperature range

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Figure 6. Monthly average minimum and maximum temperature

Figure 7. Annual precipitation pattern

Figure 8. Annual average temperature pattern

Climate stations used

(1) PITTSFIELD #2 [USC00116837], Pittsfield, IL
(2) CLARKSVILLE L&D 24 [USC00231640], Clarksville, MO

Influencing water features

Chert Exposed Backslope Woodlands are not influenced by wetland or riparian water features. Precipitation is the main source of water for this ecological site. Infiltration is moderate (Hydrologic Group B), and surface runoff is high. Surface runoff contributes some water to downslope ecological sites.

Figure 9. Hydrologic cycling in Chert Exposed Backslope Woodland ecological site.

Soil features

Soils of Chert Exposed Backslope Woodlands are in the Alfisols order, further classified as Typic Paleudalfs with moderate infiltration and high runoff potential. The soil series associated with this site includes Goss. The parent material is residuum weathered from cherty limestone, and the soils are well to somewhat excessively drained and very deep. Soil pH classes are very strongly acid to slightly acid. An abrupt textural change may be noted as a rooting restriction for the soils of this ecological site.

Figure 10. Profile sketches of soil series associated with Chert Exposed Backslope Woodland.

Table 4. Representative soil features

Parent material	(1) Residuum – chert
Surface texture	(1) Gravelly silt loam
Family particle size	(1) Clayey-skeletal
Drainage class	Well drained to somewhat excessively drained
Permeability class	Moderately slow
Depth to restrictive layer	203 cm
Soil depth	203 cm
Surface fragment cover <=3"	0%
Surface fragment cover >3"	0%
Available water capacity (Depth not specified)	2.54 cm
Calcium carbonate equivalent (Depth not specified)	0%
Electrical conductivity (Depth not specified)	0 mmhos/cm
Sodium adsorption ratio (Depth not specified)	0
Soil reaction (1:1 water) (Depth not specified)	4.5 – 6.5
Subsurface fragment volume <=3" (Depth not specified)	0 – 20%
Subsurface fragment volume >3" (Depth not specified)	0 – 14%

Ecological dynamics

The information in this Ecological Site Description, including the state-and-transition model (STM), was developed based on historical data, current field data, professional experience, and a review of the scientific literature. As a result, all possible scenarios or plant species may not be included. Key indicator plant species, disturbances, and ecological processes are described to inform land management decisions.

The MLRA lies within the tallgrass prairie ecosystem of the Midwest, but a variety of environmental and edaphic factors resulted in a landscape that historically supported upland hardwood forests, lowland mixed forests, and scattered grass and sedge meadows. Chert Exposed Backslope Woodlands form an aspect of this vegetative continuum. This ecological site occurs on south and west facing upland backslopes on well to somewhat excessively drained soils Species characteristic of this ecological site include an open canopy of oak and hickory with herbaceous vegetation.

Fire is a critical factor that maintains Chert Exposed Backslope Woodlands. Fire typically consisted of low- to moderate-severity surface fires every 15 to 25 years (LANDFIRE 2009). Ignition sources included summertime lightning strikes from convective storms and bimodal, human ignitions during the spring and fall seasons. Native Americans regularly set fires to improve sight lines for hunting, drive large game, improve grazing and browsing habitat, agricultural clearing, and enhance vital ethnobotanical plants (Barrett 1980; LANDFIRE 2009).

Drought and storm damage have also played a role in shaping this ecological site. The periodic episodes of reduced soil moisture in conjunction with the well to somewhat excessively-drained soils have favored the proliferation of plant species tolerant of such conditions. Drought can also slow the growth of plants and result in dieback of certain species. Damage to trees from wind and ice storms can vary from minor, patchy effects of individual trees to stand effects that temporarily affect community structure and species richness and diversity (Irland 2000; Peterson 2000). When coupled with fire, periods of drought and catastrophic storm damage can greatly delay the establishment and maturation of woody vegetation (Pyne et al. 1996).

Today, Chert Exposed Backslope Woodlands have been reduced from their pre-settlement extent. Sites have been subject to repeated timber harvests or have been converted to forage land. A return to the historic plant community may not be possible following extensive land modification, but long-term conservation agriculture or forest reconstruction efforts can help to restore some biotic diversity and ecological function. The state-and-transition model that follows provides a detailed description of each state, community phase, pathway, and transition. This model is based on available experimental research, field observations, literature reviews, professional consensus, and interpretations.

State and transition model

More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective text

Ecosystem states

1. Reference State - Chert Exposed Backslope Forest

2. Timber Harvest State

3. Pasture State

4. Reconstructed Oak Woodland State

T1A	-	Timber harvesting (with tree planting)
T1B	-	Cultural treatments are implemented to increase forage quality and yield
T2A	-	Cultural treatments are implemented to increase forage quality and yield
R2A	-	Site preparation, tree planting, non-native species control, and native seeding
T3A	-	Timber harvesting (with tree planting)
R3A	-	Site preparation, tree planting, non-native species control, and native seeding
T4A	-	Timber harvesting (with tree planting)
T4B	-	Cultural treatments are implemented to increase forage quality and yield

State 1 submodel, plant communities

1.1. White Oak – Black Oak/Little Bluestem – Woman’s Tobacco

1.2. White Oak – Black Oak/Fragrant Sumac/Little Bluestem

P1.1A	-	Increased fire return interval
P1.2A	-	Replacement fire

State 2 submodel, plant communities

2.1. Even-Age Managed Stand

2.2. Uneven-Age Managed Stand

2.3. High-Graded/Grazed Stand

P2.1A	-	Uneven-aged timber harvests
P2.1B	-	Implementation of rest-rotational grazing
P2.2A	-	Even-age timber harvests
P2.2B	-	Selective harvests and cattle grazing
P2.3B	-	Even-aged timber harvests
P2.3A	-	Uneven-aged timber harvests

State 3 submodel, plant communities

3.1. Smooth brome -Tall fescue-Clover Pasture

3.2. Broomsedge -Thistle-Smooth brome -Tall fescue Pasture

P3.1A	-	Grazing; overutilization of forage plants
P3.2A	-	Grazing; forage-animal balance

State 4 submodel, plant communities

4.1. Early Successional Reconstructed Woodland

4.2. Late Successional Reconstructed Woodland

P4.1A	-	Invasive species control and implementation of disturbance regimes
P4.2A	-	Drought or improper timing/use of management actions

State 1
Reference State - Chert Exposed Backslope Forest

The reference plant community is categorized as an oak forest, dominated by deciduous trees and shade-tolerant herbaceous vegetation with a large amount of chert gravel in the soil profile. The two community phases within the reference state are dependent on recurring fire intervals. The severity and intensity of fire alters species composition, cover, and extent, while regular fire intervals keep the canopy from succeeding to mesophytic, fire-intolerant species. Drought and catastrophic storm damage have more localized impacts in the reference phases, but do contribute to overall species composition, diversity, cover, and productivity.

Dominant plant species

white oak (Quercus alba), tree
black oak (Quercus velutina), tree
little bluestem (Schizachyrium scoparium), grass
woman's tobacco (Antennaria plantaginifolia), other herbaceous

Community 1.1
White Oak – Black Oak/Little Bluestem – Woman’s Tobacco

Sites in this reference community phase are an open canopy woodland. White oak and black oak are the dominant species, but hickories are common canopy associates. Trees are large (21 to 33-inch DBH), and cover is approximately 80 percent (LANDFIRE 2009). The herbaceous layer is abundant with species such as little bluestem, woman’s tobacco, Pennsylvania sedge (Carex pensylvanica Lam.), poverty oatgrass (Danthonia spicata (L.) P. Beauv. Ex Roem. & Schult.), and hairy sunflower (Helianthus hirsutus Raf.) (Nelson, 2010; NatureServe 2018). Surface fires occurring approximately every 20 years will maintain this phase, but beyond 25 years the community will shift to phase 1.2 (LANDFIRE 2009).

Dominant plant species

white oak (Quercus alba), tree
black oak (Quercus velutina), tree
little bluestem (Schizachyrium scoparium), grass
woman's tobacco (Antennaria plantaginifolia), other herbaceous

Community 1.2
White Oak – Black Oak/Fragrant Sumac/Little Bluestem

Sites in this reference community phase are a closed canopy forest, with white oak and red oak still dominant species. However, under a prolonged fire return interval the red oak may increase and sugar maple (Acer saccharum L.) encroaches in the subcanopy. Periodic surface fires will maintain this phase, but replacement fires occurring approximately every 20 years will shift the community back to phase 1.1 (LANDFIRE 2009).

Pathway P1.1A
Community 1.1 to 1.2

Pathway 1.1A – Increased fire return interval.

Pathway P1.2A
Community 1.2 to 1.1

Pathway 1.2A – Replacement fire every 20 years.

State 2
Timber Harvest State

The timber harvest state occurs when the reference state has undergone past and continued heavy logging, and in some cases grazing. Hickories often increase as a result of harvest practices and long-term fire suppression allows the woody understory to become more developed. Additionally, the absence of fire allows shade-tolerant species, such as sugar maple, to increase in abundance.

Dominant plant species

hybrid hickory (Carya), tree
sugar maple (Acer saccharum), tree

Community 2.1
Even-Age Managed Stand

This community phase is characterized by a dense forest with an underdeveloped understory and ground flora as the site has been subject to a clearcut harvest. This removal of all trees from the site not only drastically alters the biotic plant community, but it also increases soil erosion, reduces water retention capacity, alters nutrient cycling, changes the local microclimate, and destabilizes carbon (Lacroix et al. 2016). Continual timber management will maintain this phase.

Community 2.2
Uneven-Age Managed Stand

This community phase may superficially resemble the reference state, however tree age will fall between 50 and 90 years due to selective timber harvests. Periodic timber harvests via single-tree or group selection are conducted with the overall goal of producing three distinct age classes of trees intermingled across a forest stand.

Dominant plant species

oak (Quercus), tree

Community 2.3
High-Graded/Grazed Stand

Sites falling into this community phase represent forests that have been subjected to repeated, high-grade timber harvests and grazing by domestic cattle. This state exhibits an overabundance of hickory and other less desirable tree species as well as a weedy, simplified understory prone to invasion by non-native species (NatureServe 2018). The vegetation offers little nutritional value for cattle, and excessive stocking damages tree boles, degrades understory species composition, and results in soil compaction and accelerated erosion and runoff.

Dominant plant species

hybrid hickory (Carya), tree
maple (Acer), tree

Pathway P2.1A
Community 2.1 to 2.2

Pathway 2.1A – Uneven-age timber management implemented.

Pathway P2.1B
Community 2.1 to 2.3

Pathway 2.1B – High-grading and cattle grazing implemented.

Pathway P2.2A
Community 2.2 to 2.1

Pathway 2.2A – Even-age timber management implemented.

Pathway P2.2B
Community 2.2 to 2.3

Pathway 2.2B – High-grading and cattle grazing implemented.

Pathway P2.3B
Community 2.3 to 2.1

Pathway 2.3B – Cattle removed and even-age timber management implemented.

Pathway P2.3A
Community 2.3 to 2.2

Pathway 2.3A – Cattle removed and uneven-age timber management implemented.

State 3
Pasture State

The pasture state occurs when the reference state is converted to a farming system 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.) tall fescue ( Festuca arundinacea), 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 (NatureServe 2018).

Dominant plant species

smooth brome (Bromus inermis), grass
tall fescue (Schedonorus arundinaceus), grass
Kentucky bluegrass (Poa pratensis), grass

Community 3.1
Smooth brome -Tall fescue-Clover Pasture

This community is characterized by seeded cool-season grass and forbs. Species will depend upon landowner goals and objectives and may include many different grasses and forbs. Common species include smooth brome (Bromus inermis), tall fescue (Festuca arundinacea), Kentucky bluegrass (Poa pratensis), timothy (Phleum pratense), red clover ( Trifolium pratense) and white clover (Trifolium repens L.). Management inputs include control of weeds and brush. These sites are managed to ensure a proper forage/animal balance. Plants are not overutilized and have adequate rest and recovery.

Dominant plant species

tall fescue (Schedonorus arundinaceus), grass
smooth brome (Bromus inermis), grass
Kentucky bluegrass (Poa pratensis), grass
white clover (Trifolium repens), other herbaceous
red clover (Trifolium pratense), other herbaceous

Community 3.2
Broomsedge -Thistle-Smooth brome -Tall fescue Pasture

Over utilization of the pasture will result in a shift to include more undesirable species such as thistle (Cirsium spp.), broomsedge (Andropogon virginicus L.), ironweed (Vernonia gigantea), buttercup (Ranunculus spp.), ragweed (Ambrosia spp.) and blackberries (Rubus spp.). Many woody and weed species may be present depending on seed sources and level of soil disturbance. This community reflects an improper forage-to-animal balance which will negatively impact forage productivity and reproduction, soil health, and water quality. Ecological resiliency is compromised under these conditions.

Dominant plant species

broomsedge bluestem (Andropogon virginicus), grass
crabgrass (Digitaria), grass
tall fescue (Schedonorus arundinaceus), grass
smooth brome (Bromus inermis), grass
thistle (Cirsium), other herbaceous
buttercup (Ranunculus), other herbaceous
ragweed (Ambrosia), other herbaceous
ironweed (Vernonia), other herbaceous

Pathway P3.1A
Community 3.1 to 3.2

Grazing of livestock with overutilization of the forage plants.

Pathway P3.2A
Community 3.2 to 3.1

Forage plants are not overutilized and the site has a proper forage-to-animal balance.

State 4
Reconstructed Oak Woodland State

The combination of natural and anthropogenic disturbances occurring today has resulted in numerous forest health issues, and restoration back to the historic reference condition may not be possible. Woodlands are being stressed by non-native diseases and pests, habitat fragmentation, permanent changes in soil hydrology, 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; timber, fiber, and fuel products; as well as a variety of cultural activities (e.g., hiking, camping, hunting) (Millennium Ecosystem Assessment 2005; Flickinger 2010). Therefore, conservation of forests and woodlands should still be pursued. Woodland reconstructions are an important tool for repairing natural ecological functioning and providing habitat protection for numerous species associated with this site. 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 oak woodland state is the result of a long-term commitment involving a multi-step, adaptive management process.

Dominant plant species

oak (Quercus), tree

Community 4.1
Early Successional Reconstructed Woodland

This community phase represents the early community assembly from forest reconstruction. It is highly dependent on the current condition of the site based on past and current land management actions, invasive species, and proximity to land populated with non-native pests and diseases. Therefore, no two sites will have the same early successional composition. Technical forestry assistance should be sought to develop suitable conservation management plans.

Community 4.2
Late Successional Reconstructed Woodland

Appropriately timed management practices (e.g., prescribed fire, hazardous fuels management, forest stand improvement, continuing integrated pest management) applied to the early successional community phase can help increase the stand maturity, pushing the site into a late successional community phase over time. A late successional reconstructed forest will have an uneven-aged canopy and a well-developed shrub layer and understory.

Pathway P4.1A
Community 4.1 to 4.2

Pathway 4.1A – Application of stand improvement practices in line with a developed management plan.

Pathway P4.2A
Community 4.2 to 4.1

Pathway 4.2A – Reconstruction experiences a setback from extreme weather event or improper timing of management actions.

Transition T1A
State 1 to 2

Transition 1A – Timber harvesting transitions the site to the timber harvest state (2).

Transition T1B
State 1 to 3

Transition 1B – Cultural treatments to enhance forage quality and yield transitions the site to the pasture state (3).

Transition T2A
State 2 to 3

Transition 2A – Cultural treatments to enhance forage quality and yield transitions the site to the pasture state (3).

Restoration pathway R2A
State 2 to 4

Restoration 2A – Site preparation, tree planting, invasive species control, and seeding native species transition this site to the oak woodland state (4).

Transition T3A
State 3 to 2

Transition 3A – Tree planting and timber harvesting will transition the site to the timber harvest state(2).

Restoration pathway R3A
State 3 to 4

Restoration 3A – Site preparation, tree planting, invasive species control, and seeding native species transition this site to the reconstructed oak woodland state (4).

Transition T4A
State 4 to 2

Transition 4A – Fire suppression and removal of active management transitions this site to the fire-suppressed state (2).

Transition T4B
State 4 to 3

Transition 4B – Cultural treatments to enhance forage quality and yield transition the site to the pasture state (3).

Additional community tables

Supporting information

Inventory data references

No field plots were available for this site. A review of the scientific literature and professional experience were used to approximate the plant communities for this provisional ecological site. Information for the state-and-transition model was obtained from the same sources. All community phases are considered provisional based on these plots and the sources identified in this ecological site description.

Other references

Angel, J. No date. Climate of Illinois Narrative. Illinois State Water Survey, Prairie Research Institute, University of Illinois at Urbana-Champaign. Available at https://www.isws.illinois.edu/statecli/General/Illinois-climate-narrative.htm. Accessed 8 November 2018.

Barrett, S.W. 1984. Indians and fire. Western Wildlands. Spring: 17-20.

Bharati, L., K.-H. Lee, T.M. Isenhart, and R.C. Schultz. 2002. Soil-water infiltration under crops, pasture, and established riparian buffer in Midwestern USA. Agroforestry Systems 56: 249-257.

Cleland, D.T., J.A. Freeouf, J.E. Keys, G.J. Nowacki, C. Carpenter, and W.H. McNab. 2007. Ecological Subregions: Sections and Subsections of the Coterminous United States. USDA Forest Service, General Technical Report WO-76. Washington, DC. 92 pps.

Franzluebbers, A.J., J.A. Stuedemann, H.H. Schomberg, and S.R. Wilkinson. 2000. Soil organic C and N pools under long-term pasture management in the Southern Piedmont USA. Soil Biology and Biochemistry 32:469-478.

Illinois Forestry Development Council (IFDC). 2018. Illinois Forest Action Plan: A Statewide Forest Resource Assessment and Strategy, Version 4.1. Illinois Forestry Development Council and Illinois Department of Natural Resources. 80 pps.

Irland, L.C. 2000. Ice storms and forest impacts. The Science of the Total Environment 262:231-242.

Lacroix, E.M., C.L. Petrenko, and A.J. Friedland. 2016. Evidence for losses from strongly bound SOM pools after clear cutting in a northern hardwood forest. Soil Science 181: 202-207.

LANDFIRE. 2009. Biophysical Setting 4213100 North-Central Interior Dry-Mesic Oak Forest and Woodland. In: LANDFIRE National Vegetation Dynamics Models. USDA Forest Service and US Department of Interior. Washington, DC.

Leake, J., D. Johnson, D. Donnelly, G. Muckle, L. Boddy, and D. Read. 2004. Networks of power and influence: the role of mycorrhizal mycelium in controlling plant communities and agroecosystem functioning. Canadian Journal of Botany 82: 1016-1045.

Millennium Ecosystem Assessment. 2005. Ecosystems and Human Well-Being: Current States and Trends. World Resources Institute. Island Press, Washington, D.C. 948 pages.

NatureServe. 2018. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1 NatureServe, Arlington, VA. Available at http://explorer.natureserve.org. (Accessed 4 December 2019).

Nelson, P. 2010. The Terrestrial Natural Communities of Missouri. Missouri Department of Natural Resources, Missouri Natural Areas Committee. 550 pps.

Peel, M.C., B.L. Finlayson, and T.A. McMahon. 2007. Updated world map of the Köppen-Geiger climate classification. Hydrology and Earth System Sciences 11: 1633-1644.

Peterson, C.J. 2000. Catastrophic wind damage to North American forests and the potential impact of climate change. The Science of the Total Environment 262: 287-311.

Pyne, S.J., P.L. Andrews, and R.D. Laven. 1996. Introduction to Wildland Fire, Second Edition. John Wiley and Sons, Inc. New York, New York. 808 pps.

Schwegman, J.E., G.B. Fell, M. Hutchinson, G. Paulson, W.M. Shepherd, and J. White. 1973. Comprehensive Plan for the Illinois Nature Preserves System, Part 2 The Natural Divisions of Illinois. Illinois Nature Preserves Commission, Rockford, IL. 32 pps.

Skinner, R.H. 2008. High biomass removal limits carbon sequestration potential of mature temperate pastures. Journal for Environmental Quality 37: 1319-1326.

Society for Ecological Restoration [SER] Science & Policy Working Group. 2002. The SER Primer on Ecological Restoration. Available at: http://www.ser.org/. (Accessed 28 February 2017).

Taft, J.B., R.C. Anderson, L.R. Iverson, and W.C. Handel. 2009. Chapter 4: Vegetation ecology and change in terrestrial ecosystems. In: C.A. Taylor, J.B. Taft, and C.E. Warwick (eds.). Canaries in the Catbird Seat: The Past, Present, and Future of Biological Resources in a Changing Environment. Illinois Natural Heritage Survey Special Publication 30, Prairie Research Institute, University of Illinois at Urbana-Champaign. 306 pps.

Teague, W.R., S.L. Dowhower, S.A. Baker, N. Haile, P.B. DeLaune, and D.M. Conover. 2011. Grazing management impacts on vegetation, soil biota and soil chemical, physical and hydrological properties in tall grass prairie. Agriculture, Ecosystems and Environment 141: 310-322.

Undersander, D., B. Albert, D. Cosgrove, D. Johnson, and P. Peterson. 2002. Pastures for Profit: A Guide to Rotational Grazing (A3529). University of Wisconsin-Extension and University of Minnesota Extension Service. 43 pps.

United States Department of Agriculture – Natural Resources Conservation Service (USDA-NRCS). 2003. National Range and Pasture Handbook, Revision 1. Grazing Lands Technology Institute. 214 pps.

United States Department of Agriculture – Natural Resource Conservation Service (USDA-NRCS). 2006. Land Resource Regions and Major Land Resource Areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296. 682 pps.

U.S. Environmental Protection Agency [EPA]. 2013. Level III and Level IV Ecoregions of the Continental United States. Corvallis, OR, U.S. EPA, National Health and Environmental Effects Research Laboratory, map scale 1:3,000,000. Available at http://www.epa.gov/eco-research/level-iii-andiv-ecoregions-continental-united-states. (Accessed 1 March 2017).

White, J. and M.H. Madany. 1978. Classification of natural communities in Illinois. In: J. White. Illinois Natural Areas Inventory Technical Report. Illinois Natural Areas Inventory, Department of Landscape Architecture, University of Illinois at Urbana/Champaign. 426 pps.

Contributors

Lisa Kluesner
Rick Francen

Approval

Suzanne Mayne-Kinney, 12/30/2024

Acknowledgments

This project could not have been completed without the dedication and commitment from a variety of staff members. Team members supported the project by serving on the technical team, assisting with the development of state and community phases of the state-and-transition model, providing peer review and technical editing, and conducting quality control and quality assurance reviews.

List of primary contributors and reviewers.
Organization Name Title Location
Iowa Department of Natural Resources Kevin Andersen State Private Lands Biologist Fairfield, IA
Natural Resources Conservation Service Patrick Chase State Soil Scientist Des Moines, IA
Ron Collman State Soil Scientist Champaign, IL
Tonie Endres Senior Regional Soil Scientist Indianapolis, IN
Rick Francen Soil Scientist Springfield, IL
Lisa Kluesner Ecological Site Specialist Waverly, IA
Jorge, Lugo-Camacho State Soil Scientist Columbia, MO
Kevin Norwood Soil Survey Regional Director Indianapolis, IN
Stanley Sipp Resource Inventory Specialist Champaign, IL
Jason Steele Area Resource Soil Scientist Fairfield, IA
Chris Tecklenberg Acting Regional Ecological Site Specialist Hutchinson, KS
Doug Wallace ACES Ecologist Columbia, MO

Rangeland health reference sheet

Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.

Author(s)/participant(s)	Lisa Kluesner
Contact for lead author
Date	01/10/2025
Approved by	Suzanne Mayne-Kinney
Approval date
Composition (Indicators 10 and 12) based on	Annual Production