|Generations per year:||One|
The gypsy moth, Lymantria dispar, is a moth in the family Lymantriidae of Eurasian origin. Originally ranging from Europe to Asia, it was introduced to North America in the late 1860s, where it has been expanding its range ever since.
Description[edit | edit source]
The hatching of gypsy moth eggs coincides with budding of most hardwood trees. Larvae emerge from egg masses from early spring through mid-May.
Gypsy moths are dispersed in two ways. Natural dispersal occurs when newly hatched larvae hanging from host trees on silken threads are carried by the wind for a distance of up to about 1 mile, although most go less than 50 meters. Eggs can be carried for longer distances. Artificial dispersal occurs when people transport gypsy moth eggs thousands of miles from infested areas on cars and recreational vehicles, firewood, household goods, and other personal possessions. Females are flightless in most varieties, so these are the only means of spread.
Symptoms and Signs[edit | edit source]
The effects of defoliation depend primarily on the amount of foliage that is removed, the condition of the tree at the time it is defoliated, the number of consecutive defoliations, available soil moisture, and the species of host. If less than 50 percent of their crown is defoliated, most hardwoods will experience only a slight reduction (or loss) in radial growth.
If more than 50 percent of their crown is defoliated, most hardwoods will refoliate or produce a second flush of foliage by midsummer. Healthy trees can usually withstand one or two consecutive defoliations of greater than 50 percent. Trees that have been weakened by previous defoliation or been subjected to other stresses such as droughts are frequently killed after a single defoliation of more than 50 percent.
Trees use energy reserves during refoliation and are eventually weakened. Weakened trees exhibit symptoms such as dying back of twigs and branches in the upper crown and sprouting of old buds on the trunk and larger branches. Weakened trees experience radial growth reduction of approximately 30 to 50 percent.
Trees weakened by consecutive defoliations are also vulnerable to attack by disease organisms and other insects. For example, the Armillaria fungus attacks the roots, and the two-lined chestnut borer attacks the trunk and branches. Affected trees will eventually die 2 or 3 years after they are attacked.
Although not preferred by the larvae, pines and hemlocks are subject to heavy defoliation during gypsy moth outbreaks and are more likely to be killed than hardwoods. A single, complete defoliation can kill approximately 50 percent of the pines and 90 percent of the mature hemlocks. This is because conifers do not store energy in their roots; an exception is larch.
Ecology[edit | edit source]
Development and reproduction[edit | edit source]
Larvae develop into adults by going through a series of progressive moults through which they increase in size. Instars are the stages between each molt. Male larvae normally go through five instars (females, go through six) before entering the pupal stage. Newly hatched larvae are black with long hair-like setae. Older larvae have five pairs of raised blue spots and six pairs of raised brick-red spots along their backs, and a sprinkling of setae.
During the first three instars, larvae remain in the top branches or crowns of host trees. The first stage or instar chews small holes in the leaves. The second and third instars feed from the outer edge of the leaf toward the center.
When population numbers are sparse, the movement of the larvae up and down the tree coincides with light intensity. Larvae in the fourth instar feed in the top branches or crown at night. When the sun comes up, larvae crawl down the trunk of the tree to rest during daylight hours. Larvae hide under flaps of bark, in crevices, or under branches - any place that provides protection. When larvae hide underneath leaf litter, mice, shrews, and Calosoma beetles can prey on them. At dusk, when the sun sets, larvae climb back up to the top branches of the host tree to feed. When population numbers are dense, however, larvae feed continuously day and night until the foliage of the host tree is stripped. Then they crawl in search of new sources of food.
The larvae reach maturity between mid-June and early July. They enter the pupal stage. This is the stage during which larvae change into adults or moths. Pupation lasts from 7 to 14 days. When the population is spread out and running low, pupation can take place under flaps of bark, in crevices, under branches, on the ground, and in other places where larvae rested. During periods when population numbers are dense, pupation is not restricted to locations where larvae rested. Pupation will take place in sheltered and non-sheltered locations, even exposed on the trunks of trees or on foliage of nonhost trees. Sometimes the caterpillars create flimsy cocoons made of silk strands holding the leaf together, while others do not cover their pupae in cocoons, but rather hang from a twig or tree bark, like butterfly pupae do.
The brown male gypsy moth emerges first, flying in rapid zigzag patterns searching for females. The male gypsy moths are diurnal unlike most moths, which are nocturnal. When heavy, black-and-white egg-laden females emerge, they emit a chemical substance called a pheromone that attracts the males. The female lays her eggs in July and August close to the spot where she pupated. Then, both adult gypsy moths die. The European and most Russian forms of the gypsy moth have flightless females. Although they have large wings, the musculature is not developed. However, the Japanese gypsy moth females do fly and are attracted to lights. During outbreaks they have been known to fly to ships in port and lay their eggs on the ships.
The egg is the overwintering stage. After an acclimation stage, eggs can withstand freezing temperatures. The longer they are chilled in winter, the less heating is required for their hatch in spring. Gypsy moth egg masses are typically laid on branches and trunks of trees, but egg masses may be found in any sheltered location. Egg masses are buff colored when first laid but may bleach out over the winter months when exposed to direct sunlight and weathering. As the female lays them, she covers them with hair-like setae from her abdomen. Many individuals find these hairs irritating, and they may offer the eggs some protection. Egg masses contain from a couple of hundred to about 1200 eggs.
North American Introduction[edit | edit source]
The gypsy moth was introduced into the United States in 1868 by a French scientist, Leopold Trouvelot, living in Medford, Massachusetts, who enjoyed raising many types of caterpillars including silkworms. It is now one of the most notorious pests of hardwood trees in the Eastern United States. The first outbreak there occurred in 1889. By 1987, the gypsy moth had established itself throughout the Northeast USA and southern Quebec and Ontario. The insect has spread south into Virginia and West Virginia, and west into Michigan and Wisconsin. Infestations have also occurred sporadically in Utah, Oregon, Washington, California, and British Columbia.
Since 1980, the gypsy moth has defoliated over 1,000,000 acres (4,000 km²) of forest each year. In 1981, a record 12,900,000 acres (52,200 km²) were defoliated. This is an area larger than Rhode Island, Massachusetts, and Connecticut combined.
In wooded suburban areas, during periods of infestation when trees are visibly defoliated, gypsy moth larvae crawl up and down walls, across roads, over outdoor furniture, and even inside homes. During periods of feeding they leave behind a mixture of small pieces of leaves and frass, or excrement. During outbreaks, the sound of chewing and frass dropping is a continual annoyance.
Gypsy moth populations usually remain at very low levels but occasionally populations increase to very high levels which can result in partial to total defoliation of host trees for 1-3 years.
Host plants[edit | edit source]
Gypsy moth larvae prefer oaks, but may feed on several hundred different species of trees and shrubs, both hardwood and conifer. In the East the gypsy moth prefers oaks, aspen, apple, sweetgum, speckled alder, basswood, gray and paper birch, poplar, willow, and hawthorn, although other species are also affected. The list of hosts will undoubtedly expand as the insect spreads south and west. The gypsy moth avoids ash, tulip-tree, American sycamore, butternut, black walnut, catalpa, flowering dogwood, balsam fir, arborvitae, American holly, and shrubs such as mountain laurel and rhododendron, but will feed on these in late instars when densities are extremely high. Older larvae feed on several species of hardwood that younger larvae avoid, including cottonwood, hemlock, Atlantic white cypress, and the pines and spruces native to the East.
- Abies (Fir)
- Acer (Maple)
- Alnus (Alder)
- Betula (Birch)
- Carya (Hickory)
- Chamaecyparis (False cypress)
- Cornus (Dogwood)
- Crataegus (Hawthorn)
- Fagus (Beech)
- Fraxinus (Ash)
- Juglans (Walnut)
- Liquidumbar (Sweetgum)
- Liriodendron (Tuliptree)
- Malus (Apple)
- Picea (Spruce)
- Pinus (Pine)
- Platinus (Sycamore)
- Populus (Poplar)
- Prunus (Stone Fruits)
- Quercus (Oak)
- Salix (Willow)
- Thuja (Arborvitae)
- Tilia (Linden, Basswood)
- Tsuga (Hemlock)
- Ulmus (Elm)
Control[edit | edit source]
- Cultural controls: Stands of trees that are predominantly oak and grow on poor, dry sites (such as sand flats or rock ridges) are frequently stressed and often incur repeated, severe defoliations. Trees growing under these conditions frequently possess an abundance of structural features such as holes, wounds, and deep bark fissures that provide shelter and habitats for gypsy moth larvae and aid their survival.
Appropriate action will be determined by an anticipated occurrence of gypsy moth defoliation, by characteristics of the stand, and by the economic maturity of the stand. Foresters refer to treatments discussed here as "thinnings." Thinnings are cuttings made in forest stands to remove surplus trees (usually dominant and subdominant size classes) in order to stimulate the growth of trees that remain.
Predefoliation treatments: When gypsy moth defoliation is anticipated, but not within the next 5 years, predefoliation thinning to selectively remove preferred-host trees can reduce the severity of defoliation, increase the vigor of residual trees, and encourage seed production and stump sprouting. Thinnings should not be conducted in fully stocked stands that will reach maturity within the next 6 to 15 years. Thinning results in a short-term "shock effect" to residual trees. This shock effect, coupled with defoliation-caused stress, renders trees vulnerable to attack by disease organisms such as Armillaria.
In fully stocked stands that will reach maturity within the next 16 or more years, two kinds of thinning can be applied. The method of thinning should depend on the proportion of preferred host species present. If more than 50 percent of the basal area in a stand is preferred host species (mainly oaks), presalvage thinning should be applied. Presalvage thinning is designed to remove the trees most likely to die (trees with poor crown condition) from stress caused by gypsy moth defoliation. If less than 50 percent of the basal area in a stand is in preferred host species, sanitation thinning can be applied to reduce further the number of preferred host trees. This will result in fewer refuges for gypsy moth larvae and in improved habitats for the natural enemies of the gypsy moth.
Treatment during outbreaks: If defoliation is current or is expected within the next 5 years, thinnings should be delayed because of potential "shock effect." High-value stands can be protected by applying pesticides. In low-value stands or those that are at low risk (less than 50 percent basal area in preferred host species), protective treatments are optional.
Post-outbreak treatments: After a defoliation episode, the land manager or woodlot owner should pursue efficient salvage of dead trees, but should delay decisions about additional salvage, regeneration, or other treatments for up to 3 years. At the end of 3 years, most defoliation-caused mortality will be complete and the need for treatments can be assessed on the basis of damage level, current stocking conditions, and stand maturity.
- Trapping: Every year, over 100,000 pheromone traps are placed in uninfested portions of the US in order to detect new infestations that occasionally arise when people inadvertently transport life stages into uninfested areas (e.g., egg masses on recreational vehicles). When captures are positive for several consecutive years, this indicates that a population is establishing itself.
- Pesticides: The most commonly used chemical pesticides currently registered by the U.S. Environmental Protection Agency (EPA) for use against the gypsy moth contain carbaryl, diflubenzuron, and acephate. Malathion, methoxychlor, phosmet, trichlorfon, and synthetic pyrethroids (permethrin) have also been registered by EPA for control of gypsy moth, but are used infrequently. The bacterial pesticide Bacillus thuringiensis ('Bt') is also used.
Diflubenzuron represents a new class of pesticides called insect growth regulators. It kills gypsy moth larvae by interfering with the normal molting process. Diflubenzuron has no effect on adult insects.
The decision to use pesticides is influenced by a number of factors:
- The number of visible egg masses.
- The percentage of preferred hosts in a mixed stand of trees (50 percent or more of oak).
- Whether trees already have dead or dying branches, especially near the top branches or crown.
- Whether the property is located adjacent to wooded areas heavily infested with gypsy moths.
- Predators and parasites: Natural enemies play an important role during periods when gypsy moth populations are sparse. Natural enemies include parasitic and predatory insects such as wasps, flies, ground beetles, and ants; many species of spider; several species of birds such as chickadees, blue jays, nuthatches, towhees, and robins; and approximately 15 species of common woodland mammals, such as the white-footed mouse, shrews, chipmunks, squirrels, and raccoons. Predation by small mammals (mice and shrews) is the largest source of mortality in low density gypsy moth populations and this mortality is apparently critical in preventing outbreaks. Calosoma, a ground beetle of European origin, cuckoos, and flocking birds, such as starling, grackles, and red-winged blackbirds, are attracted to infested areas in years when gypsy moth populations are dense.
Diseases caused by bacteria, fungi, or viruses contribute to the decline of gypsy moth populations, especially during periods when gypsy moth populations are dense and are stressed by lack of preferred foliage. Wilt disease caused by a particular nucleopolyhedrosis virus (NPV) that is specific to the gypsy moth is the most devastating of the natural diseases. NPV causes a dramatic collapse of outbreak populations by killing both the larvae and pupae. Larvae infected with wilt disease are shiny and hang limply in an inverted "V" position. Infection with NPV is the most common source of mortality in high density populations and NPV epizootics usually cause the collapse of populations. Since the 1980s, the fungus Entomophaga maimaiga has also had a large impact on gypsy moth populations in North America.
- Biocontrols (microscopic): Microbial and biological pesticides contain living organisms that must be consumed by the pest. Microbials include bacteria, viruses, and other naturally occurring organisms; biologicals include manmade synthetics of naturally occurring organisms. These pesticides should be applied before the larvae reach the third stage or instar of development. As they mature, larvae become more resistant to microbial pesticides and are, therefore, more difficult to kill.
Nucleopolyhedrosis virus (NPV), a naturally occurring organism, has been developed as a microbial pesticide. It is presently registered under the name "Gypchek" and is available for use in USDA Forest Service sponsored suppression programs. NPV and Gypcheck are specific to the gypsy moth.
Bacillus thuringiensis (Bt) is microbial and biological. It is the most commonly used pesticide. In addition to being used against the gypsy moth, Bt is used against a number of other pests, including the western spruce budworm, spruce budworm, and tent caterpillar. When Bt is taken internally, the insect becomes paralyzed, stops feeding, and dies of starvation or disease.
Chemical pesticides are contact poisons in addition to being stomach poisons. The timing of the chemical application is less critical to the successful population reduction of the pest than the timing of the application of the microbials and biologicals. Chemical pesticides can affect non-target organisms and may be hazardous to human health.
- Timing: Weather affects the survival and development of gypsy moth life stages regardless of population density. For example, temperatures of -20°F, (-29°C.) lasting from 48 to 72 hours can kill exposed eggs; alternate periods of freezing and thawing in late winter and early spring may prevent the over wintering eggs from hatching; and cold, rainy weather inhibits dispersal and feeding of the newly hatched larvae and slows their growth.
|Microbial and chemical pesticides commonly used for gypsy moth control|
|Active ingredient||Trade name||Remarks|
|Bacillus thuringiensis||Dipel Thuricide||Registered for aerial and ground application. Available under a variety of trade names. Toxic to other moth and butterfly larvae. Can be used safely near water.|
|Acephate||Orthene||Registered for aerial and ground application. Available under a variety of trade names. Toxic to bees and some gypsy moth parasites. Commonly used from the ground to treat individual trees.|
|Carbaryl||Sevin||Registered for aerial and ground application. Available under a variety of trade names. Toxic to bees and gypsy moth parasites. At one time, the most widely used chemical in gypsy moth control programs.|
|Diflubenzuron||Dimilin||A restricted-use pesticide that can be applied only by certified applicators.|
References[edit | edit source]
- McManus, M.; Schneeberger, N.; Reardon, R.; and Mason, G. 1992. Gypsy Moth. Forest Insect & Disease Leaflet 162 U.S. Department of Agriculture Forest Service. Public Domain per U.S. Govt. policy. The authors of which cite these references:
- Podgwaite, J.D. 1979. Diseases of the gypsy moth: How they help to regulate populations. Agric. Handb. 539. Washington, DC: U.S. Department of Agriculture. p.2–15.
- McManus, Michael L.; Houston, David R.; Wallner, William E. 1979. The homeowner and the gypsy moth: Guidelines for control. Home and Gard. Bull. 227. Washington, DC: U.S. Department of Agriculture. p.4–33.
- Gansner, D.A.; Herrick, O.W.; Mason, G.N.; Gottschalk, K.W. 1987. Coping with the gypsy moth on new frontiers of infestation.Southern Journal of Applied Forestry Research. 11: 201–209.
Further information[edit | edit source]
- Andreadis TG, Weseloh RM. 1990. Discovery of Entomophaga maimaiga in North American gypsy moth, Lymantria dispar. Proceedings of the National Academy of Sciences of the United States of America 87 (7): 2461-2465.
- Barbosa P, Greenblatt J. 1979. Suitability, digestibility and assimilation of various host plants of the gypsy moth Lymantria dispar L (Lepidoptera, Lymantriidae). Oecologia 43 (1): 111-119 1979
- Barbosa P, Waldvogel M, Martinat P, et al. 1983. Developmental and reproductive performance of the gypsy moth, Lymantria dispar (L) (Lepidoptera, Lymantriidae), on selected hosts common to mid-atlantic and southern forests. Environmental Entomology 12 (6): 1858-1862.
- Bogdanowicz SM, Wallner WE, Bell J, et al. 1993. Asian gypsy moths (Lepidoptera, Lymantriidae) in North America - evidence from molecular data. Annals of the Entomological Society of America 86 (6): 710-715.
- Dwyer G, Elkinton JS. 1993. Using simple-models to predict virus epizootics in gypsy-moth populations. Journal Of Animal Ecology 62 (1): 1-11.
- Elkinton JS, Healy WM, Buonaccorsi JP, Boettner GH, Hazzard AM, Smith HR, Liebhold AM. 1996. Interactions among gypsy moths, white-footed mice, and acorns. Ecology 77 (8): 2332-2342.
- Gould JR, Elkinton JS, Wallner WE. 1990. Density-dependent suppression of experimentally created gypsy moth, Lymantria dispar (Lepidoptera, Lymantriidae), populations by natural enemies. Journal of Animal Ecology 59 (1): 213-233.
- Liebhold AM, Halverson JA, Elmes GA. 1992. Gypsy moth invasion in North America - a quantitative analysis. Journal of Biogeography 19 (5): 513-520.
- Myers, Judith H. 1993. Population Outbreaks in Forest Lepidoptera. American Scientist 81, 240-251.
- Rossiter MC. 1991. Maternal effects generate variation in life-history - consequences of egg weight plasticity in the gypsy moth. Functional Ecology 5 (3): 386-393.
- Weseloh RM, Andreadis TG. 1992. Epizootiology of the fungus Entomophaga maimaiga, and its impact on gypsy moth populations. Journal of Invertebrate Pathology 59 (2): 133-141.