
The European corn borer was first discovered in North America in 1919 and in Manitoba in 1948. It has been an economic pest in Manitoba corn fields on a sporadic basis. The European corn borer will feed on sweet, grain and silage corn. In addition, the European corn borer has a wide variety of other host plants including tomatoes, potatoes, beans, sugar beets and many species of large stemmed flowers and weeds.
In Manitoba there is only one generation of corn borer per year. In some years, as much as ten per cent of the population will attempt a second generation although this generation will be unsuccessful. Infestations in Manitoba are quite variable from year to year with some areas experiencing heavy infestations while other areas have little or no damage caused by the corn borer.
The European corn borer has four stages in its life cycle.
Adult
Adult moths are buff-coloured with brown markings on its wings (Figure 1). The male moths are darker with darker markings than the female moths. The adult moths emerge from the pupae in late June and early July. The adults are 0.5 inch (12 mm) long with a wingspan of 1.0 inch (25 mm) and are strong fliers. Newly emerged adults seek out dense areas of vegetation, preferring grassy ditches where they congregate and mate. After mating, females lay eggs during calm, warm summer evenings on the underside of corn leaves near the mid-rib.
Figure 1
Egg
Each egg mass consists of 10 to 40 eggs. Each female can lay two egg masses per evening, for up to ten evenings. Newly laid eggs are white and overlap, resembling fish scales (Figure 2). Just before the eggs hatch, they appear black. The dark appearance is caused by the dark heads of the young borers inside the eggs (Figure 3). The eggs hatch within three to seven days, depending upon temperature.
Figure 2
Figure 3
There are five larval instars of the corn borer. The first two instars (Figure 4) are whitish with black heads and feed within the whorl and cause shothole and window pane damage (Figure 5). The first two instars complete development in seven to ten days. The third instar larvae bores into the stalk. Once inside the stalk, it is too late to achieve effective chemical control. The later instars (third to fifth) feed within the stalk and ear shanks, disrupting the normal movement of nutrients, which results in decreased yield. Tunneling and boring may permit secondary infection and damage by rotting of the stalk and ear. Older larvae (Figure 6) are flesh coloured with black spots and may also feed on silks, kernels and cobs. Once they are finished feeding, the mature larvae overwinter in corn stalks, cobs and plant debris on the soil surface.
In the spring, mature larvae turn into pupae to complete the life cycle (Figure 7).
Figure 4
Figure 5
Figure 6
Figure 7
The European corn borer causes damage in several ways. The first sign of damage is the pinhole damage. If the larvae establishes within a plant it may cause several types of damage. The most severe damage is stalk breakage prior to harvest (Figure 8). Another type of damage is ear drop where cobs fall to the ground. The final type of damage may be the least obvious but can cause significant yield loss. By restricting nutrient flow in the plant, yield is affected by the production of smaller cobs (Figure 9).
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Figure 8 |
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Figure 9 |
Cultural Control
Deep plowing of stubble can kill some of the overwintering corn borer larvae, or cause them to die of exposure on the surface at pupation time in the spring. These practices will reduce overwintering larvae, but the larvae that are not killed can still cause a severe infestation under suitable climatic conditions. However, soil and moisture conservation must also be considered when managing insect populations. In Manitoba, time of planting does not alter the severity of the corn borer infestation due the much longer oviposition (egg-laying) period. Control of alternate weed hosts may help reduce population levels. Mowing of grassy ditches and headlands where adult moths congregate will provide less favourable locations for adults to rest and mate, possibly causing them to migrate to other areas away from the corn field. Rotation will also help control populations.
Biological Control
There are many natural enemies that will feed on corn borer larvae. These include lady beetle adults and larvae, syrphid or hover fly larvae and green lacewing larvae. Natural enemies do not provide control in outbreak situations. In non-outbreak situations it is important to not apply chemical control measures unless the economic threshold is reached so that the populations of beneficial insects will not be affected.
Chemical Control
Insecticides should only be applied when economic thresholds (ET) have been surpassed. To determine whether the population in a given field has reached the economic threshold, it is important to scout the field. Insecticide recommendations can be found in Manitoba Agriculture and Food’s Guide to Crop Protection.
Use the Management Worksheet and Economic Threshold table below to determine whether chemical control measures are necessary. Field scouting should begin in early July. Fields should be prioritized by planting date and relative maturity. Older fields should be scouted first. In each field, check 10 locations (10 plants at each location) for egg masses and young larvae. The larvae are most commonly found in the midrib and leaf axil. At each location pull open the whorl to check for larvae feeding within the whorl. If the majority of larvae have bored into the stalk, do not apply insecticides as they are ineffective once the larvae have entered the stalk. If no larvae or egg masses are found, repeat scouting every five to seven days. Continue scouting until larvae start to tunnel into the stalk or the end of July if no egg masses/larvae are found.
Bacillus thuringiensis (Bt) corn is a type of corn that has been genetically modified. Bt is a bacterium that has insecticidal properties when ingested by certain types of insects. Bt is a naturally occurring soilborne bacterium that produces crystal-like proteins that selectively kill certain groups of insects. The protein crystals are insect stomach poisons that are activated by the insects digestive enzymes to form the toxin. Through the process of biotechnology, scientists have inserted certain Bt genetic material (DNA) into the corn plant’s DNA. DNA is the genetic material that controls expression of a plant’s (or animal) traits. Since the Bt is right in the corn plant, the only way insects are exposed to it, is eating the corn plant. Bt corn does not control feeding by most insects other than the European corn borer. Aphids, spider mites and grasshoppers will not be affected by Bt corn, although some cutworms may be suppressed. Bt corn has little effect on beneficial insects. There are many potential benefits to Bt Corn, the most obvious being control of the European corn borer. Other potential benefits include yield protection, reduced insecticide use, reduced control costs, proper timing of control, safety to wildlife and insect predators, reduced frequency of disease and reduced stalk lodging. There are also potential limitations to Bt corn. These include the unpredictability of corn borer densities, no guaranteed economic return, variable yield performance, marketing restrictions as a result of perceptions of transgenic crops and resistance of European corn borer to Bt.
The European corn borer may have the potential to develop resistance to the Bt proteins found in Bt corn. This is pesticide resistance even though nothing has been sprayed. If all acres of corn were planted to Bt corn it would not take very long before resistance developed and the Bt corn was rendered ineffective. This may occur if a small percentage of European corn borers survive on Bt corn. These resistant moths would then breed with moths that are not resistant and the resistance may not be passed on. If the only corn borers to survive are all resistant to Bt, then the resistance will be passed on to the next generation of corn borers. In time, the Bt corn would no longer be able to control the European corn borer. Resistance is known to occur to Bt sprays in other agricultural areas. Measures must be taken to ensure that resistance does not develop or is delayed. There are several approaches that may be taken. The most simple approach is to not plant Bt corn every year. Use Bt hybrids only in fields where the risk from corn borer infestation warrants the price premium for the seed. In addition to this approach is the preservation of refuges of non-Bt corn for the corn borer to feed on. While it may seem illogical to try to preserve the population, remember that the European corn borer has many hosts and the pest cannot be eradicated. Therefore, the next best option is to ensure that the corn borer remains susceptible to Bt. Refuges are areas where susceptible corn cultivars are planted. Research from corn growing areas of the United States recommend the following ratios of non-Bt corn for refuges:
When no insecticide application will be made to control pests - 20 percent
It is critical that all growers retain refuges for corn borer. Planting refuges can be done in several ways. Refuges may be planted in blocks. These blocks must be accessible to the corn borer (do not isolate the refuge in the centre of the field). These blocks may be placed along field margins, along ditches or in blocks within the field. How important are the refuges? Consider the following numbers from U.S. studies. Reducing the refuge from 10 to five percent increases the probability of resistance developing from 37 percent to 74 percent. Increasing the refuge from 10 to 20 percent reduces the probability of resistance developing from 37 percent to less than one percent (Figure 10).

Figure 10
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Economic threshold (Corn borers/plant)
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Control Costs 1 ($/Acre) |
Crop Value ($/Acre) | |||||
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150 |
200 |
250 |
300 |
350 |
400 |
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6 |
1.00 |
0.75 |
0.60 |
0.50 |
0.43 |
0.38 |
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9 |
1.50 |
1.12 |
0.90 |
0.75 |
0.64 |
0.56 |
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12 |
2.00 |
1.50 |
1.20 |
1.00 |
0.86 |
0.75 |
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15 |
2.50 |
1.88 |
1.50 |
1.25 |
1.07 |
0.94 |
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18 |
3.00 |
2.25 |
1.80 |
1.50 |
1.29 |
1.13 |
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21 |
3.50 |
2.63 |
2.10 |
1.75 |
1.50 |
1.32 |
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24 |
4.00 |
3.01 |
2.40 |
2.00 |
1.72 |
1.51 |
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27 |
4.50 |
3.38 |
2.70 |
2.25 |
1.93 |
1.70 |
| 1Control costs = insecticide price ($/acre) and application costs ($/acre) | ||||||
For further information, contact your GO representative.