
The European earwig is native to Europe, western Asia, and northern Africa, but has been introduced to North America, Australia and New Zealand.
The European earwig was first observed in North America at Seattle, Washington in 1907. It spread quickly, and was reported from Oregon in 1909, British Columbia in 1919, and California in 1923. It reached Rhode Island in 1911, New York in 1912, and most other provinces and northern states in the 1930s and 1940s. Presently it occurs south to North Carolina, Arizona and southern California, but due to its preference for temperate climates it is unlikely to become abundant in the southeastern states. Also, it is not very tolerant of arid environments, but survives where irrigation is practiced. However, it is often intercepted in Florida and other southeastern states, arriving in shipments of produce and other products, as well as hitchhiking on motor homes and other vehicles (Paul Choate, personal comunication).
Other earwigs are abundant in North America, but few are as numerous as European earwig, and none are as damaging. The ringlegged earwig, Euborellia annulipes (Lucas), and the African earwig, Euborellia cincticollis (Gerstaecker), are probably the only other species of concern to crop producers. Ringlegged earwig is widespread, but African earwig is limited to southwestern states. Neither species is native to North America, though ringlegged earwig has become the dominant earwig in Florida.
Adults bear a set of cerci at the tip of the abdomen. Adults can use the cerci in defense, twisting the abdomen forward over the head or sideways to engage an enemy, often another earwig. The pronounced cerci are the most distinctive feature of earwigs; in the male the cerci are strongly curved whereas in the female they curve only slightly. The forceps of some males are 3/16 inch (5 mm) long, while others have forceps 3/8 inch (9.5 mm) long (Jacobs 2009).
Egg: The egg is pearly white in color and oval to elliptical in shape. The egg measures 1.13 mm in length and 0.85 mm in width when first deposited, but absorbs water, swells, and nearly doubles in volume before hatching. Eggs are deposited in a cell in the soil, in a single cluster, usually within 5 cm of the surface. Mean number of eggs per cluster is reported to range from 30 to 60 eggs in the first cluster. The second cluster, if produced, contains only half as many eggs. Duration of the egg stage under winter field conditions in British Columbia averages 72.8 days (range 56-85 days). The second or spring brood of eggs requires only 20 days to hatch. Eggs are attended by the female, who frequently moves the eggs around the cell, and apparently keeps mold from developing on the eggs (Buxton and Madge 1974). Females guard their eggs from other earwigs, and fight with any intruders.
adult female with eggs and young
Nymph: The nymphal stages, four in number, have the same general form as adults except that the wings increase in size with maturity. The cerci are present in all instars, growing in size with each molt. The body color darkens, gradually changing from grayish brown to dark brown, as the nymph matures. The legs are pale throughout. The wing pads are first evident in the fourth instar. Mean head capsule width is 0.91, 1.14, 1.5, and 1.9 mm in instars 1-4, respectively. Mean body length is 4.2, 6.0, 9.0, and 9-11 mm, respectively. The number of antennal segments is 8, 10, 11, and 12 in instars 1-4. Mean duration (range) of instars under laboratory temperatures of 15-21°C is 12.0 (11-15), 10.2 (8-14), 11.2 (9-15), and 16.2 (14-19) days for instars 1-4. However, development time is considerably longer under field conditions, requiring 18-24, 14-21, 15-20, and about 21 days for the corresponding instars. Young nymphs are guarded by the mother earwig, who remains in or near the cell where the eggs are deposited until the nymph's second instar is attained.
One generation is completed annually, and overwintering occurs in the adult stage. In British Columbia, eggs are deposited in late winter, eggs hatch in May, and nymphs attain the adult stage in August. Overwintering females may also produce an additional brood; these eggs hatch in June and also mature by the end of August (Lamb and Wellington 1975). In Washington, these events occur about one month earlier (Crumb et al. 1941). Only a single brood of eggs is produced in colder climates, such as Quebec (Tourneur and Gingras 1992).
Social behavior is weakly developed in European earwig. Males and females mate in late summer or autumn, and then construct a subterranean tunnel (nest) in which they overwinter. The female drives the male from the nest at the time of oviposition. Eggs are manipulated frequently, apparently cleaning them to prevent growth of fungi. She will relocate the eggs in an attempt to provide optimal temperature and humidity for the eggs. Although the female normally keeps the eggs in a pile, as the time for hatching approaches she spreads the eggs in a single layer. After hatching, females continue to guard the nymphs and provide them with food. Food is provided by females carrying objects into the nest, and by regurgitation. Thus, there is parental care, but no cooperative brood care (Lamb 1976).
The most comprehensive treatment of European earwig biology is by Crumb et al. (1941), although the publications by Jones (1917) and Fulton (1924) are informative.
Seedlings and plants providing the earwigs with good shelter, such as the heads of cauliflower, the stem bases of chard, and the ears of corn, are particularly likely to be eaten, and also to be contaminated with fecal material. Among flowers most often injured are dahlia, carnation, pinks, sweet william, and zinnia. Ripe fruit such as apple, apricot, peach, plum, pear, and strawberry are sometimes reported to be damaged.
The European earwig is reported to consume aphids, spiders, caterpillar pupae, leaf beetle eggs, scale insects, spiders, and springtails as well as vegetable matter. Aphid consumption is especially frequent and well documented (McLeod and Chant 1952, Buxton and Madge (1976a & b, Mueller et al. 1988). In addition to the higher plants mentioned above, earwigs consume algae and fungi, and often consume vegetable and animal matter in equal proportions (Buxton and Madge 1976a).
Cultural control. On residential property or in small gardens, persistent trapping can be used to reduce earwig abundance, though this approach is challenging if the initial earwig density is high. Boards placed on the soil will be attractive to earwigs seeking shelter. Even more earwigs will accumulate if there are narrow grooves or channels in the board. Moistened, rolled-up newspaper placed in the garden in the evening and disposed of in the morning makes a convenient earwig trap for home gardens. A particularly effective technique is to fill a flower pot with wood shavings and invert the pot over a short stake that has been driven into the soil. Traps can also be placed in trees because earwigs favor convenient shelters after foraging for food during the evening.
Biological control. Several natural enemies are known, including some that were imported from Europe in an attempt to limit the destructive habits of this earwig in North America. Some authors have suggested that the most important natural enemy is the European parasitoid Bigonicheta spinipennis (Meigen) (Diptera: Tachinidae), which has been reported to parasitize 10-50% of the earwigs in British Columbia. Others, however, report low incidence of parasitism (Lamb and Wellington 1975). Another fly, Ocytata pallipes (Fallén) (Diptera: Tachinidae) also was successfully established, but causes little mortality. Under the cool, wet conditions of Oregon, Washington, and British Columbia, the fungi Erynia forficulae and Metarhizium anisopliae also infect earwigs (Crumb et al. 1941, Ben-Ze'ev 1986). The nematode Mermis nigrescens appears to be an important mortality factor in Ontario, where 10-63% of earwigs were infected during a 2-year period (Wilson 1971). However, this nematode has not been reported from earwigs elsewhere. Avian predation can be significant (Lamb 1975).
Chemical control. Residual foliar insecticides and baits containing toxicant can be used to suppress earwigs. Of numerous baits evaluated, Crumb et al. (1941) suggested that wheat bran flakes plus toxicant and a small amount of fish oil was an optimal for killing these insects. Fulton (1924) believed fish oil unnecessary but suggested addition of glycerin and molasses. Commercial products are rarely formulated specifically for earwigs because they rarely are a severe problem. Rather, products sold for grasshoppers, cutworms, slugs, and sowbugs are applied for earwig control. Bait is most effective if applied in the evening.
Florida Insect Management Guide for ornanmentals
Florida Insect Management Guide for vegetables
Florida Insect Management Guide for household earwigs
Authors: John L. Capinera, University of Florida
Photograph: Jim Kalisch, University of Nebraska-Lincoln; Cheryl Moorehead; Nabokov
Graphic: Paul E. Skelly, Division of Plant Industry
Project Coordinator: Thomas R. Fasulo,
University of Florida
Publication Number: EENY-483
Publication Date: October 2010.
Copyright 2010 University of Florida
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Department of Entomology and Nematology
Division of Plant Industry
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