![]() ![]() Left: E. maimaiga resting spores. Right: E. maimaiga conidia. A. Hajek (both) Entomophaga maimaiga
|
![]() Gypsy moth cadaver hanging from tree trunk. Donald Specker |
AppearancePresence of E. maimaiga may be determined by late instar gypsy moth larvae which, when infected with this fungus, die hanging vertically from tree trunks with prolegs extended laterally. The cadavers subsequently fall to the bases of trees. Hyphal bodies are found within infected insects and spore-producing mycelium can grow on the outside of cadavers but decomposes after conidia are produced and actively ejected from cadaver surfaces. Resting spores are about 30 micrometers in diameter and may be found inside late instars of infected gypsy moths. |
Trees, both broadleaf and coniferous, of forests and urban and suburban areas (see distribution map below).
High titers of E. maimaiga resting spores have been documented at the bases of trees where infected gypsy moth larvae have died.

Map courtesy of USDA Forest Health
Protection, Morgantown Field Office
Based on lab results, E. maimaiga appears to be quite specific to the family that includes gypsy moth, although it can cause low levels of infection in a number of other species.
During a field study, the only cadavers that were found on trees were gypsy moth larvae killed by E. maimaiga. At locations where there were active epizootics of E. maimaiga occurring in gypsy moth populations, more than 1500 insects of 53 difference species were collected. Of those 1500 individuals, only one individual of a lasiocampid and one individual from the Noctuidae were infected with E. maimaiga.
Species in the Entomophthorales have several life stages:
- The conidia are relatively short-lived. Spores are actively discharged from cadavers and can immediately germinate and cause infection.
- Hyphal bodies occur within infected insects and mycelium grows on the outside of cadavers.
- Resting spores are produced internally in late instars and must undergo a period of dormancy.
From E. maimaiga epizootics occurring in North American gypsy moth populations in 1989 and 1990, it became clear that this fungus was capable of becoming an important mortality factor. Whereas nuclear polyhedrosis viral epidemics in gypsy moth populations require a high population density, E. maimaiga can cause epizootics at lower densities. In release studies done in 1991 and 1992, this fungus appeared to spread readily, even in less wet years, and persisted 3 years later. Gypsy moths were also still present in these studies, but there was a high degree of fungal infection documenting long-term persistence of this fungus in an area with the potential for long-term control. In a 1995 study of E. maimaiga released against gypsy moth in residential areas, only the control plots had high levels of defoliation.
Data from 1996 indicates that gypsy moth defoliation declined more than 85% from 1995 levels over 11 states. The most dramatic case is in Virginia where 1996 defoliation was nonexistent compared with 850,000 acres in 1995. There is general consensus among scientists and pest managers that E. maimaiga is probably responsible for the decline. However it is not known if this level of fungus activity will continue. It appears that E. maimaiga has spread throughout much of the area considered to be generally infested by gypsy moth, the only exception being the transition area into which the insect is spreading for the first time.
E. maimaiga has been highly variable and unpredictable. Consequently, the use of environmentally safe and effective insecticides will continue to be important tools to reduce damage caused by gypsy moth outbreaks, and several points should be emphasized:
Each spring, infection by E. maimaiga is initiated when resting spores germinate to produce infective germ conidia. Because high titers of resting spores have been found in the organic layer of the soil at the bases of trees, it is assumed that disruption of this layer, e.g., turning over the soil at the tree base, might decrease the titer of resting spores near the soil surface, and thus would decrease the level of infection from these spores.
Although E. maimaiga has not yet been tested for its susceptibility to fungicides, there is the potential that use of fungicides especially around the bases of trees could cause mortality among E. maimaiga resting spores.
Studies are planned to evaluate the susceptibility of E. maimaiga to the fungicides to which it might be exposed in the forest and urban landscape.
Not available commercially at this time.
Thanks to Ann Hajek for reviewing this page, supplying photographs and suggestions, and making valuable additions.
Hajek, A.E. (1996) Entomophaga maimaiga: A Fungal Pathogen of Gypsy Moth in the Limelight. In Proceedings of the Cornell Community Conference on Biological Control.
Schneeberger, Noel F. 1996. Gypsy moth populations plummet in 1996 while "The Fungus" skyrockets. Gypsy Moth News, 42: 1-2.
©All material is protected by Section 107 of the 1976 copyright
law.
Copyright is held by Cornell University.
Use of this material for educational purposes is encouraged. Please notify the
editors of such use and cite the
author (if credited on the page you are using). A recommended form for citing this website is:
Weeden, C.R., A. M. Shelton, and M. P. Hoffman. Biological Control: A Guide to Natural Enemies in North America.
http://www.nysaes.cornell.edu/ent/biocontrol/ accessed (date).