PROTECTING WISCONSIN'S BIODIVERSITY

 
 
   
 
Community Name Global Rank State Rank Community Group

Oak Woodland

SAV_OW02.jpg

 

 

9135.jpg

Photo by Drew Feldkirchner

 

Counties with Mapped NHI Occurrences

Oak woodland is a type of savanna that is intermediate between more open oak opening and more closed canopied oak forests. It tends to be dominated by members of white oak group, especially white oak, sometimes with bur oak, and locally in southwestern Wisconsin, chinquapin oak. Red oak, black oak, and shagbark hickory may also be present and can sometimes account for 50% relative cover or more of the tree layer. Canopy closure can vary widely. The best quality sites have a canopy 41-65% closure but can vary from 30-80% closure. "Canopy closure" is the proportion of shrub and ground layer that is covered in shade or shade flecks at noon on a sunny day.

Oak woodlands historically experienced near-annual surface fires. As a result, the subcanopy is very sparse in good quality sites, though fire-suppressed sites often contain mesophytic species such sugar maple, red maple, ironwood, hackberry, American elm, and bitternut hickory. The shrub layer is also typically sparse but may include low growing species like low bush honeysuckle (Diervilla lonicera), snowberry (Symphoricarpos albus or S. occidentalis), blueberry (Vaccinium spp.), huckleberry (Gaylussacia baccata), New Jersey tea (Ceanothus americanus), and lead plant (Amorpha canescens).

The groundlayer in oak woodlands is often dominated by a matrix of sedges like Pennsylvania sedge and savanna running sedge (Carex siccata), sometimes also with a variety of other graminoids that thrive under dappled light conditions such as bottlebrush grass (Elymus hystrix), silky wild-rye (Elymus villosus), and wide-leaved panic grass (Dichanthelium latifolium). Forbs overlap significantly with oak openings and oak forest, but some of the best indicators include upland boneset (Eupatorium sessilifolium), prairie alumroot (Heuchera richardsonii), two-flowered Cynthia (Krigia biflora), veiny pea (Lathyrus venosus), pale vetchling (Lathyrus ochroleucus), blunt-leaved sandwort (Moehringia lateriflora), wood betony (Pedicularis canadensis), eastern shooting-star (Primula meadia), yellow-pimpernel (Taenidia integerrima), Culver's-root (Veronicastrum virginicum), Carolina vetch (Vicia caroliniana), and Short's aster (Symphyotrichum shortii). Additional oak woodland indicator species can be found in the Coarse-level Monitoring Protocol for Oak Woodlands (Carter et al, 2023).

Oak woodlands can occur in a variety of landscape settings, usually in sites that allowed them to persist with frequent fire but not so severe as to convert them to prairie or oak opening. Examples include cooler slope aspects adjacent to prairies and oak openings, knolls and ridgetops surrounded by mesic to dry-mesic forest, and upland islands surrounded by wetlands.

 
 
 

Oak woodlands can be differentiated from oak openings by their higher degree of canopy closure, more dappled light, and more a continuous canopy. In contrast, oak openings tend to have a more open, less continuous canopy and significant areas of full sun. Oak woodlands tend to have a groundlayer that thrives in dappled light and usually lacks many of the prairie species present in oak openings. Mature trees in oak woodlands usually lack the short boles and wide-spreading lower limb architecture found in oak openings, but instead have somewhat intermediate growth forms between oak opening and the tall, straight, forest-grown trees found in more closed-canopy forests.

Oak woodlands can be differentiated from oak barrens by their canopies usually dominated by white oak, and locally bur oak, often with red oak, black oak, and shagbark hickory. In contrast, oak barrens are usually dominated by black or Hill’s oak, sometimes with pines co-dominant. Oak woodlands also tend to occur on sandy loam to clay loam soils, whereas oak barrens usually occur on sand.

Closed canopy oak woodlands degraded by fire suppression or grazing can be difficult to differentiate from southern dry and dry-mesic forests. The best approach is to look for woodland indicators that may persist on more open ridgetops, knolls, south- or west-facing slopes, and along trails and edges.

Species of Greatest Conservation Need (SGCN) are associated with habitats (or natural communities) and places on the landscape. Understanding relationships among SGCN, natural communities and ecological landscapes help us make decisions about issues affecting SGCN and their habitat and how to respond. Download the Wildlife Action Plan association score spreadsheet to explore rare species, natural communities and ecological landscape associations

Conservation actions respond to issues or threats, which adversely affect species of greatest conservation need (SGCN) or their habitats. Besides actions such as restoring wetlands or planting resilient tree species in northern communities, research, surveys and monitoring are also among conservation actions described in the Wisconsin Wildlife Action Plan because lack of information can threaten our ability to successfully preserve and care for natural resources.