Dillon P. Golding1,2, Francis A. Reith1,3, and Jonathan O. C. Kubesch1,3
- Virginia Tech School of Plant and Environmental Sciences, Blacksburg, VA
- Hoot Owl Hollow Farm, Woodlawn, VA
- Country Home Farms, Pembroke, VA
Editor’s Note: The imperial data in this article applies to Virginia, but similar results can be expected in Kentucky.
Native grasslands in the Midsouth previously existed in a mosaic of plant communities across moisture and fertility regimes (Noss, 2013; Campbell, 2012). These grasslands persisted through a variety of edaphic, moisture, fire, herbivory, and human dynamics. The arrival of Europeans brought land use change, the removal of elk (Cervus canadensis) and bison (Bison bison) herds, and the arrival of cattle. These shifts in the fundamental drivers of these grassland ecosystems led to shifts in many native grasslands. While many native plants disappeared from the landscape, some persisted in modern plant communities.
Some of the native species that make up remaining grasslands persist despite the deleterious effects of early European settlement. These species survive because of their anatomy, management, or ecological strategy. For instance, species with lower-positioned meristems can regrow more effectively following overgrazing than species with higher-positioned meristems. Given that most pastures are managed at shorter heights than most traditional grasslands, these low-growing native grasses can persist within modern grazed ecosystems.

Similarly, native grasslands only used seasonally are more likely to persist following a grazing event than grasslands subject to year-round grazing (Figure 1). These grasses display either competitor or ruderal ecological strategies where they can handle the disturbance inherent to cattle grazing as well as the limited resources in herbaceous plant communities. Some especially persistent competitor or ruderal species might even disperse to other pastures from native grasslands.
Two of these species include splitbeard bluestem (Andropogon ternarius) and little bluestem (Schizachyrium scoparium). In Virginia, both species have a coefficient of conservation of 5, which suggests moderate conservative ecological behavior (DeBerry et al., 2020). These species are thus more so competitor species than ruderal ones. These species are seen on drier soils with acidic to average soil fertility throughout the Upper South (Campbell, 2012). Their meristems are closer to the soil level than species like big bluestem (Andropogon gerardii) or Indiangrass (Sorghastrum nutans), which allows them to survive intense grazing events. Cattle are known to graze these grasses (Leithead et al., 1971).
Continue reading Emergence rates of native splitbeard bluestem and little bluestem from a hay transfer microcosm








