FIDL Forest Insect
& Disease
Leaflet 163

U.S. Department
of Agriculture
Forest Service

Red Oak Borer

D.E. Donley,1 and R.E. Acciavatti2


1Research Entomologist, Northeastern Forest Experiment Station, U.S. Department of Agriculture, Forest Service Delaware Ohio.
2Entomologist, Forest Insect and Disease Management, State and Private Forestry, Northeastern area, U.S. Department of Agriculture, Forest Service, Delaware, Ohio.
3Coleoptera: Cerambycidae

The red oak borer, Enaphalodes rufulus (Haldeman)3, is an important member of the oak borer complex that permanently damages the wood of living oak trees and causes a decrease in lumber grade. The loss in grade can amount to 40 percent of the current tree value, which, at today's prices, is about $80 per thousand board feet for factory grade lumber in terms of reduced quality caused by larval tunnels. About 38 percent of the oak wood used for lumber, cooperage, and veneer in the Eastern United States is affected.

The red oak borer is native to North America, where it occurs naturally from southeastern Canada and Maine to Florida, and west to Minnesota, Iowa, Oklahoma, and Texas. The distribution map (fig. 1) presents all known county collection records, with the exception of Brewster and Jeff Davis Counties in Texas. This borer also has been found in ornamental nursery stock and shade trees outside its natural range.

figure 1
Figure 1.-Range of the red oak borer in the United States.

The red oak borer has been found in many oak species. Economic loss occurs when borer tunnels and subsequent wood overgrowths in attacked trees are distributed on the grading surfaces of boards and veneer. Wood-inhabiting insects such as carpenterworms, timberworms, and carpenter ants use red oak borer tunnels to gain entry into oaks. These other pests extend and increase the damage begun by the red oak borer. Decay organisms also gain entry into oak heartwood through borer tunnels.

Hosts

Most oaks (Quercus spp.) in Eastern North America are attacked by the borer. The most common hosts are northern red oak. (Q. rubra L.), black oak (Q. velutina Lam.), and Scarlet oak (Q. coccinea Muenchh.). Less commonly damaged are white oak (Q. alba L.), post oak (Q.stellata Wangenh.), pin oak (Q. palustris Muenchh.), bur oak (Q. macrocarpa Michx.), overcup oak (Q. lyrata Walt.), and laurel oak (Q. laurifolia Michx.).

Damage

Certain specific external signs indicate internal red oak borer damage in host trees: extruded frass (fig. 2), discolored bark patches (fig. 3), wet spots (fig. 4), wood slivers (fig. 5), and exit holes (fig. 6). These surface indicators have been associated with different stages of larval development during the insects' 2-year life cycle, and therefore can be associated with defects in lumber and other wood products.

The fine larval frass (fig. 2) is found during the first fall and winter after eggs hatch. Wet spots (fig. 3) and medium-sized larval frass can be found during the first spring and early summer. Discolored bark patches (fig. 4) and large quantities of larval frass occur in the second fall and winter (fig. 7). Wood slivers are extruded in the spring and early summer just before the adult emerges (fig. 5). The adult exits through an oval hole which it chews in the bark (fig. 6).

figure 2 figure 3 figure 4
Figure 2.-Frass accumulates
red oak borer attack site
Figure 3.-Discoloration around
a red oak borer attack site
Figure 4.-Sap flow at an early red
oak borer wound causes "wet spots" (pins delineate egg-laying site)

figure 5 figure 6 figure 7
Figure 5. -Slivers are the remains
of a "plug" constructed by the overwintering larva and pushed
out of the tunnel during the
second spring activity period.
Figure 6. -An oval exit hole is made through the bark near the initial attack site. Figure 7. -Frass accumulates base of an attacked tree.

Life Stages

The red oak borer has a 2-year synchronous life cycle. The pest has been studied in Pennsylvania, West Virginia, Ohio, Kentucky, Indiana, Illinois, and Missouri (fig. 8). In nearly all cases adults emerged in odd-numbered years.

figure 8
Figure 8. -Life history of the red oak borer in the North Central United States

The adults (fig. 9) are nocturnal and can be found from mid-June to mid-August. The sex ratio in natural populations is nearly 1 to 1. Mating takes place on the host tree and the female lays an average of 110 eggs. The eggs are attached with an adhesive in cracks, and under lichen patches and vines on host trees. Often, as many as 95 percent of the eggs hatch.

The young larvae begin boring directly through the bark and spend their first year in the phloem and sapwood making small (2 by 3 by ½ in.) (5 by 7.5 by 1.2 cm.) tunnels (fig. 10). The 2-year-old larvae make larger mines (7 by 3 by ½ in.) (15.5 by 7.5 by 1.2 cm.), and tunnel into the heartwood to construct a pupal cell (fig. 11). The adult emerges near the original oviposition site by gnawing an oval hole through the bark.

figure 9 figure 10 figure 11
Figure 9. -Red oak borer adult Figure 10. -Longitudinal view of overgrown 1-year -old larval feeding tunnels Figure 11.-Two-year-old larval feeding mines and pupal chamber.

Natural Control

Figure 12- Woodpecker excavations for red oak borers.
figure 12
Woodpeckers are the most important recognized natural control agents of the red oak borer, often reducing larval numbers by 40 percent. Winter feeding activity by the hairy woodpecker, Dendrocopus villosus, and the downy woodpecker, D. pubescens, is most successful against first year larvae because these larvae overwinter in shallow furrows in the inner bark. The success of woodpecker at the predation on second year larvae (fig. 12) within the wood depends on the placement of the woodpecker work relative to the site where the borer entered the wood. Excavation by woodpeckers at the entrance site can reduce adult red oak borer emergence by only 16 percent, but excavation away from the entrance site can result in 40- to 86-percent reduction.

Predation by the formicid ants, Aphaenogaster flemingi M.R. Smith and A. treatae Forel, also provides some degree of natural control.

Applied Control

Borer impact studies showed that only about half of the borer-caused defects produce lumber or veneer degrade. The remaining defects produce no degrade because of their size, location, or association with other degrade-producing factors such as rot, knots, and wane. When the grader disregarded half the red oak borer-caused defects, lumber grade improved and borer impact was almost eliminated. Therefore, any control practice which reduces borer damage by 50 percent will eliminate most borer-caused degrade.

Silvicultural control of the red oak borer has been achieved by removing infested trees from timber stands. Population reductions of 95 percent have been achieved over a 5-year period by this approach. Cultural controls are aimed at decreasing borer numbers in pole-size stands of red, black, scarlet, and white oaks, which reduces the chances of subsequent borer attack in the residual stand throughout its rotation.

References

Berry, F.H. 1978. Decay associated with wounds in living oaks. U.S. Department of Agriculture Forest Service Research Note NE-268, 2 p.

Donley, D.E. 1974. Wood borer losses in Appalachian oak. Southern Lumberman 229:115-118.

Donley, D.E., and D.P. Worley 1976. Insect impact on production of oak timber. Southern Lumberman (December), p.63-66.

Donley, D.E. 1978. Oviposition by the red oak borer, Enaphalodes rufulus Coleoptera:Cerambycidae. Annals Entomological Society of America 71(4):496-498.

Hay, C.J. 1972a. Red oak borer (Coleoptera:Cerambycidae) emergence from oak in Ohio. Annals Entomological Society of America 65(5):1243-1244.

Hay, C.J. 1972b. Woodpecker predation on red oak borer in black, scarlet and northern red oak. Annals Entomological Society of America 5(6):1421-1423.

Hay, C.J. 1974. Survival and mortality of red oak borer larvae on black, scarlet and northern red oak in eastern Kentucky. Annals Entomological Society of America 67(6):981-986.


U.S. GOVERNMENT PRINTING OFFICE; 1980 0-325-427
November 1980
Formatted for the Internet September 1997