White-tailed deer have increased in abundance and expanded their geographic
range in North America over the past century, and now exist at higher dens
ities than they have in the past several hundred years. This is having nume
rous impacts on the forest ecosystems they inhabit. Regional recruitment fa
ilure of eastern hemlock (Tsuga canadensis) and northern white cedar (Thuja
occidentalis) trees can be explained in part by deer browsing. Deer also h
ave significant negative effects on understorey plants, including wild lily
-of-the-valley (Maianthemum canadense) and white-flowered trillium (Trilliu
m grandiflorum). Long-term studies of primary, old-growth forest stands rev
eal a 48-81 per cent herb and shrub species loss accompanying increases in
deer density. Graminoids, ferns and club mosses were more likely to persist
in these stands than plants in all other taxonomic groups. Deer also exhib
it indirect effects on forest communities by reducing host plant densities
or altering forest structure. Because of their numerous direct and indirect
effects on other species, and because of the magnitude of these effects, w
hite-tailed deer act as a keystone herbivore. Natural regulation and maximu
m sustained yield management approaches have failed to alleviate deer impac
ts on forest ecosystems, but an ecosystem-based management approach offers
promise.