Cades Cove, located within Great Smoky Mountains National Park, is 1 of my favorite places in the world. I visited Cades Cove during June of 2017 and saw lots of deer, a few black bears, a turkey, and an herd of tame horses. It’s 1 of the best places to see wildlife east of the Mississippi. Cades Cove is known for its high density of white-tailed deer and is 1 of many areas where deer herbivory and its effect on plant species diversity and abundance has been studied. High density deer populations reduce tree regeneration and alter plant species composition and forest successional patterns. Areas where deer are abundant can also see a shift in natural communities to an alternate state, while plant species diversity becomes reduced, influencing other species of wildlife. Results of studies on the interaction between deer and plant community vary, depending upon geographical location. Some species thrive or can at least survive in high density deer locations, while these same species in a different geographical location my suffer. I’ll review some of these studies below.




Scientists studying the effect of deer herbivory on plant species composition use exclosures, or in other words they construct deer proof fences on certain plots to prevent deer from feeding on the plants inside the fence. They then compare plant composition and abundance inside and outside the fence. A study at the Clemson Experimental Forest found that after 2 years the difference between inside and outside exclosures was negligible. The differences aren’t noticeable until 5-20 years after the exclosure is constructed. At Callaway Gardens near Columbus, Georgia deer exclosures were in use for 20 years. Here, there were significant differences between the inside and outside of the enclosures. Inside the exclosures strawberry bush (Eunonymous americanus not to be confused with the strawberry people eat–Fragaria virginianus) and greenbriar, 2 favorite deer foods, grew taller and more dense than outside the exclosure. There was also an increase in red maple, black cherry, white oak, and sassafras inside the exclosure. Outside the exclosures there was an increase in sweetgum, wax myrtle, hop hornbeam, shining sumac, water oak, and willow oak. Black cherry benefitted from the absence of deer at this location, but at a site in northwest Pennsylvania, this species was found to be resistant to deer browsing.
Violet responds differently to deer herbivory at different locations as well. Scientists studying deer herbivory on the upper peninsula of Michigan found deer eradicated violets, but at Cades Code, though it is often eaten by deer, violet still regenerates. The scientists in Michigan identified “winners” and “losers” among plants in high density deer sites. “Winners included wind pollinated sedges and grasses in the Poa genus, along with hazelnut, blueberry, wood anemone, and wood fern. “Losers” in addition to violets were forbs such as big leaf aster, blue beard lily, strawberry, and thimbleberry. In some areas of Wisconsin deer can reduce tree sapling abundance by 90%, and they can eliminate white cedar and red oak. Oddly enough, yellow birch trees require moderate deer population densities. This species didn’t regenerate if deer populations were too low or too high.
The effects of deer herbivory were studied in a forest located in northwest Pennsylvania. The forest consisted of sugar maple, striped maple, black cherry, fire cherry, beech, and sweet birch. Tree regeneration failed in 25%-40% of clear cut plots. Species of trees that were browse resistant included beech, black cherry, striped maple, ash, and hackberry. A number of common bird species were absent from Pennsylvania forests with high deer population densities. This list includes wood peewees, cerulean warblers, yellow-billed cuckoos, and indigo buntings.
Ironically, heavy deer populations can accelerate forest successional patterns. By feeding upon pioneer species of plants, deer reduce competition for space with species that normally don’t dominate until later stages of forest succession.
References:
Thrift, J.
“Effects of White-Tailed Deer Herbivory on Forest Plant Communities”
Clemson University Thesis 2007
Wiegmann, S.; and D. Waller
“Fifty Years of Change in Northern Upland Forest Understory. Identity and Traits of “Winner” and “Loser Plant Species”
Biological Conservation 129 2006