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| GYPSY MOTH     Lymantria dispar (L.) -- Lepidoptera, Lymantriideae  [Also named Porthetria dispar  (L.) ]   (Contacts)     ----- CLICK on Photo to enlarge &
  search for Subject Matter with Ctrl/F.                GO TO ALL:  Bio-Control Cases   
   Biological
  Control          A
  biological control project was organized by the U. S. Department of Agriculture,
  Bureau of Entomology in 1905 and extensive foreign exploration for
  parasitoids and predators was carried out in Europe, Japan, North Africa and
  Asia at various intervals since that time (Doane & McManus 1981).  This was the first major classical
  biological control project against a forest insect, directed by Dr. L. O.
  Howard, Chief of the Bureau of Entomology. 
  DeBach (1974) revealed that a large number of young American
  entomologists were employed on the gypsy moth project, some becoming famous
  later on, e.g., P. H. Timberlake (uncle of President Richard Nixon), H. S.
  Smith, W. R. Thompson and J. D. Tothill.         
  The gypsy moth project has revealed that (1) insect disease was
  recognized as an important biological control factor, (2) the sequence theory
  of natural enemies was introduced by W. F. Fiske, (3) a number of future
  important contributors to biological control were trained on the project (H.
  S. Smith, W. R. Thompson and W. D. Tothill), (4) sleeve cages were invented
  as well as other equipment and techniques that are still in use today and (5)
  L. O. Howard and W. F. Fiske were the first to clearly distinguish between
  those causes of mortality that act in relation to the density of the
  population and those that do not.  L.
  O. Howard also stimulated the Canadian interest in biological control in the
  early 1900's by making available facilities and scientific assistance from
  the Melrose Highlands Parasite Laboratory of the U. S. Bureau of Entomology.          
  Early importations of natural enemies occurred between 1905-14 and
  again between 1922-33.  While some
  collections were made in Japan, attention focused on Europe where temporary
  field laboratories were placed wherever gypsy moth outbreaks were sufficient
  to permit the rearing of parasitoids from a large number of hosts.  Frequent shipments of parasitoids and
  predators were made to the gypsy moth laboratory at Melrose Highlands,
  Massachusetts and this resulted in the liberation of >690,000 living
  insects of more than 45 species during this period (Dowden 1962).  The enormous importation and multiple
  release program enabled two larval/pupal predators, two egg parasitoids, six
  larval parasitoids and one pupal parasitoid to become established in the New
  England states.  The two egg
  parasitoids were also subject to either large scale rearing releases in the
  case of Ooencyrtus kuwanae (How.), or to large
  scale relocation releases in the case of Anastatus
  disparis Ruschka.  Most of the establishments occurred
  rapidly after the initial field releases but the tachinids Parasetigena silvestris (R.-D.) and Exorista larvarum (L.) were not recovered until 1937 and 1940
  respectively and the chalcidid Brachymeria
  intermedia (Nees) was only
  recovered in 1965.           
  Biological control by established parasitoids and predators in New
  England was limited and large scale aerial applications of DDT were used
  until the early 1960's.  Since 1960
  renewed interest in the search for additional natural enemies has extended explorations
  in Europe, Japan, Morocco, India, Iran and Korea (Doane & McManus
  1981).  Since 1963 the USDA
  Agricultural Research Service Beneficial Insects Research Laboratory has
  continued to receive gypsy moth natural enemies in their quarantine facilities
  and have been able to distribute more than 200,000 individuals of about 60
  species to other State and Federal facilities for culture, study and field
  release.  From 1966 until 1971, the
  Gypsy Moth Methods Improvement Laboratory at Otis Air Force Base in Massachusetts
  was charged with the development of rearing procedures for the imported
  natural enemies.  From 1963-71 in
  conjunction with the New Jersey Department of Agriculture about 7 million
  parasitoids of 17 species were reared and released in the forests of New
  Jersey and Pennsylvania.  Then from
  1971-77 a Gypsy Moth Parasite Distribution Program was established in which
  the New Jersey Dept. of Agriculture and the University of Maryland reared and
  released an additional two million parasitoids of 18 species throughout the
  New England states.  Since the late
  1970's more new parasitoids and a predator from Japan and Korea and from the
  Indian gypsy moth, Lymantria
  obfuscata Walk., have been
  imported (Coulson et al. 1986).  More
  than 100,000 individuals of nine new species or strains have been released in
  the field in Delaware, Massachusetts and Pennsylvania.         
  Although much knowledge of the biology and rearing methods of the
  imported parasitoids was gained during this massive program of importation,
  propagation and release, it has resulted in the addition of only a single
  pupal parasitoid, Coccygomimus
  disparis (Vier.) to the
  complex of 10 species established during the initial importation
  program.  This has prompted Tallamy
  (1983) to compare the establishment of gypsy moth parasitoids with island
  biogeography theory, suggesting that a dynamic equilibrium now exists between
  further introductions and the extinction of established parasitoids.  In the last 30 years two of the
  parasitoids that were initially established, Anastatus disparis
  and Exorista larvarum have become very rare,
  while two pupal parasitoids Brachymeria
  intermedia and C. disparis have become established.  However, the main reasons for the failure
  to establish additional parasitoids in recent years are the parasitoids'
  requirements for suitable alternative overwintering hosts for their second
  generation each year and the fact that several of the parasitoid species
  released during the 1960's were not closely associated with gypsy moth as a
  principal host in their areas of origin (Dahlsten & Mills 1999).         
  The failure of the established natural enemies to control expanding
  outbreaks of the gypsy moth encouraged attempts during the 1970's to augment
  the impact of previously established species.  Through inundative releases of Cotesia melanoscelus
  (Ratz.), Weseloh & Anderson (1975) were able to show significantly
  increased rates of parasitism but this had little influence on foliage
  protection or egg mass counts for the following generation.  On the other and several other inundative
  releases of this and other species failed to provide any evidence of
  increased parasitism in comparison to control plots (Doane & McManus
  1981).  The combined release of
  parasitoids and pathogens has been used as a method of augmentation.  Wollam & Yendol (1976) were able to
  show a synergistic effect of the release of C. melanoscelus
  in plots treated with a double application of low concentration Bacillus thuringiensis over plots treated with each of these
  natural enemies alone.  The resultant
  reduction in defoliation and subsequent egg mass densities has more recently
  been attributed to the retarding effect of B. thuringiensis
  on host larval growth which exposes the younger larvae to parasitism for a
  longer period of time (Weseloh et al. 1983). 
  A similar effect of C.
  melanoscelus in conjunction
  with viral treatments is unlikely to occur since this parasitoid avoids
  oviposition in moribund host larvae (Versoi & Yendol 1982).   Augmentation         
  Augmentation through use of microbial pathogens has been of
  considerable importance against gypsy moth with significant advances in
  recent years.  Early trials with B. thuringiensis in the 1960's were not effective in
  providing foliage protection; but the discovery of improved strains (Dubois
  1985b) and successive improvements in formulation and application technology
  during the late 1970's and early 1980's led to greater success.  The results of aerial applications during
  the 1970's remained highly variable but a recommendation of double application
  of low concentrations was developed and used operationally for the first time
  on a large scale in 1980.  This also
  met with limited success but further experimental work in the early 1980's
  (Dubois 1985a) indicated that the use of higher concentrations and acrylamide
  stickers could provide not only good foliage protection but also could reduce
  subsequent egg mass densities significantly with a single application.  This development reduced the cost of B. thuringiensis applications and has been used operationally
  with success on 40-70% of the 1.3-1.5 million ha. of hardwood forest treated
  since 1983.   Virus
  Deployment         
  Many field trials have been conducted with virus sprays against gypsy
  moth both in North America and Europe (Cunningham 1982).  An NPV virus strain (Hamden standard)
  isolated from a natural epizootic in Connecticut in 1967 forms the basis for
  the commercially produced "Gypchek" that was registered for use
  against gypsy moth in North America in 1978. 
  However, early trials of the baculovirus produced erratic results and
  while continued improvements in formulation and application have produced
  more positive results, it has never been accepted for operational use
  (Podgwaite 1985).  Reasons for this
  are the relatively low virulence of the virus, its rapid degradation on
  foliage in the field and the more recent successes with the use of B. thuringiensis.     Conclusions         
  Dahlsten & Mills (1999) point out that the gypsy moth program has
  been spectacular in both the scale and the continued enthusiasm with which it
  has been conducted, but that the results have been disappointing and serve as
  a good example of the failure of classical biological control in situations
  where the introduced pest is also severe in its region of origin.  Therefore the search for natural enemies
  in areas where gypsy moth is not a pest, in non-outbreak populations or from
  related non-pest Lymantria
  species may prove to be a better strategy.         
  For further details on biological control efforts and biologies of
  host and natural enemies, please see the following (Fiske 1910, Howard 1910,
  Howard & Fiske 1911, Burgess 1915, Burgess & Collins 1915, Culver
  1919, Tothill 1919, Crossman 1922, 1925; Escaleva 1926, Webber & Schaffner
  1926, Muesebeck & Dohanian 1927, Burgess & Crossman 1929, Lepiney
  1933, Schaffner 1934, Baeta-Neva & Azeveda 1944, Templado 1957, Hitchcock
  1959, Tadic & Bin
ev 1959, Dowden 1961a,b; Tadic 1962, Salatic
  1963, Bjegovic 1964, Leonard 1966, 1967; Clausen 1978)     REFERENCES: [Additional references may be found at:   MELVYL Library ]   Baeta
  Neves, C. M. & F. A. e Silva. 
  1944.  Nota sobre a aplicacao da
  luta biologica na companha da Lymantria.  Bol. Junta Nac. Cortica (Lisbon) 63:  101-03.   Bellows, T. S. & T. W. Fisher (eds.).  1999. Handbook
  of Biological Control:  Principles and
  Applications.  Academic Press, San
  Diego, New York.  1046 p.   Bjegovic, P. 
  1964.  The dependence of the
  sex ratio of Anastatus disparis Ruschka on the phase
  of embrionic development of the host. 
  Zast. Bilja 15:  569-76.   Burgess, A. F. 
  1915.  Report on the gypsy moth
  work in New England.  U. S. Dept.
  Agric. Bull. 204.  32 p.   Burgess, A. F. & C. W. Collins.  1915. 
  The Calosoma beetle (Calosoma sycophanta) in New England.  U. S. Dept. Agric. Bull. 251. 
  40 p.   Burgess, A. F. & S. S. Crossman.  1929. 
  Imported insect enemies of the gypsy moth and the brown-tail moth.  U. S. Dept. Agric. Tech. Bull. 86.  147 p.   Clausen, C.
  P.  1978.  Lymantriidae.  In:  C. P. Clausen (ed.), Introduced Parasites
  and Predators of Arthropod Pests and Weeds: A World Review.  U. S. Dept. Agric., Agric. Handbk. No.
  480.  545 p.   Coulson, J. R., R. W. Fenster, P. W. Schaefer,
  L. R. Ertle, J. S. Kelleher, & L. D. Rhoads.  1986.  Exploration for
  and importation of natural enemies of the gypsy moth, Lymantria dispar
  (L.) (Lepidoptera: Lymantriidae), in North America:  an update.  Proc. Ent.
  Soc. Wash. 88:  461-75.   Crossman, S. S.  1922.  Apanteles melanoscelus, an imported parasite of the gypsy moth.  U. S. Dept. Agric. Bull. 1028.  25 p.   Crossman, S. S.  1925.  Two impoirted egg
  parasites of the gypsy moth, Anastatus
  bifasciatus Fonsc. and Schedius kuvanae Howard.  J.
  Agric. Res. 30:  643-75.   Culver, J.
  J.  1919.  A study of Compsilura concinnata, an imported tachinid parasite of the gypsy
  moth and the brown-tail moth.  U. S.
  Dept. Agric. Bull. 776.  27 p.   Cunningham, J. C.  1982.  Field trials with
  baculoviruses:  control of forest
  insect pests, p. 335-386.  In:  E. Kurstak (ed.), "Microbial and Viral Pesticides.  Marcel Dekker, Inc., New York.  720 p.   Dahlsten, D.
  L. & N. J. Mills.  1999. 
  Biological Control of Forest Insects. 
  In:  Bellows, T. S.
  & T. W. Fisher (eds.), Handbook of
  Biological Control:  Principles and
  Applications.  Academic Press, San
  Diego, New York.  1046 p   DeBach, P.  1974.  Biological Control by Natural
  Enemies.  Cambridge University Press,
  London & New York.  323 p.   Doane, C. C. & M. L. McManus.  1981. 
  The gypsy moth:  research
  toward integrated pest management. 
  USDA Forest Service Tech. Bull. 1584. 
  757 p.   Dowden, P. B. 
  1961a.  The persistence of
  gypsy moth parasites in heavy sprayed areas of Cape Cod, Msssachusetts.  J. Econ. Ent. 54:  873-75.   Dowden, P. B. 
  1961b.  The gypsy moth egg
  parasite Ooencyrtus kuwanai in southern Connecticut
  in 1960.  J. Econ.
  Ent. 54:  876-78.   Dowden, P. B. 
  1962.  Parasites and predators
  of forest insects liberated in the United States through 1960.  USDA, Forest Service, Agric. Handbook No.
  226, 70 pp.   Dubois, N. R. 
  1985a.  Recent field studies on
  the use of Bacillus thuringiensis to control the
  gypsy moth (Lymantria dispar L.).  Proc. Symposium Microbial Control of
  Spruce Budworms and Gypsy Moths.  USDA
  For. Serv. GTR-NE-100. p. 83-85.   Dubois, N. R. 
  1985b.  Selection of new more
  potent strains of Bacillus thuringiensis for use against
  gypsy moth and spruce budworm.  Proc.
  Symposium Microbial Control of Spruce Budworms and Gypsy Moths, USDA For.
  Serv. GTR-NE-100.  p. 99-102.   Escalera,
  F. M. de la.  1926.  Un neuvo ensayo para combatir en Argelia
  la plaga de Lymantria dispar (Lep.).  3rd Internatl. Cong. Ent. Proc. 2:  414-16.   Fiske, W. F. 
  1910.  Parasites of the Gypsy
  and Brown-tail Moths Introduced Into Massachusetts.  Wright & Potter Printing Co., Boston.  56 p.   Hitchcock, S. W.  1959.  Number of fall
  generations of Ooencyrtus kuwanae (How.) in gypsy moth
  eggs.  J. Econ. Ent. 52:  764-65.   Howard, L. O. 
  1910.  Technical results from
  the gypsy moth laboratory. I.  The
  parasites reared or supposed to have been reared from the eggs of the gypsy
  moth.  U. S. Dept. Agric. Bur. Ent.
  Tech. Ser. 19, pt. 1.  12 p.   Howard, L. O. & W. F. Fiske.  1911. 
  The importation into the United States of the parasites of the gypsy
  moth and the brown-tail moth.  U. S.
  Dept. Agric. Bur. Ent. Bull. 91:  344
  p.   Leonard, D. E. 
  1966.  Brachymeria intermedia
  (Nees) (Hymenoptera: Chalcididae) established in North America.  Ent. News 77:  25-7.   Leonard, D. E. 
  1967.  Parasitism of gypsy moth
  in Connecticut by Brachymeria
  intermedia.  J. Econ. Ent. 60:  600-01.   Lepiney, J.
  de.  1933.  Le role de la direction des eaux et forets du Maroc et de
  l'Institut Scientifique Cherifien dans la lutte biologique entreprise contre Lymantria dispar a laaide de Schedius
  kuwanae.  5th Internatl. Cong. Ent. Proc. (1932) 5:  807-12.   Muesebeck, C. F. W. & S. M. Dohanian.  1927. 
  A study in hyperparasitism, with particular reference to Apanteles melanoscelus (Ratzeburg). 
  U. S. Dept. Agric. Dept. Bull. 1487. 
  35 p.   Podgwaite, J. D.  1985.  Gypchek:  past and future strategies for use.  Proc. Symposium:  Microbial Control of Spruce Budworms and Gypsy Moths.  USDA For. Serv. GTR-NE-100. p. 91-93.   Salatic, S. 
  1963.  Results of
  investigations of some factors of effectiveness of gypsy moth egg
  parasites.  Zastita Bilja,
  Belgrade 14:  693-99.   Schaffner, J.
  V., Jr.  1934. 
  Introduced parasites of the brown-tail and gypsy moths reared from
  native hosts.  Ann. Ent. Soc.
  Amer. 27:  585-92.   Tadic,
  M.  1962.  Numerical
  relationship between Anastatus
  disparis R. and Ooencyrtus kuwanae How. in certain localities of Yugoslavia.  Agron. Glasnik 5-7:  548-52.   Tadic, M. & B. Bin
ev.  1959.  Gubar. 
  Resultati rada na njegovom prou
avanju i
  suzbyanju kod nas u toku 1958 Godine. 
  Plant Protect. 1959:  51-59.   Tallamy, D. W. 
  1983.  Equilibrium biogeography
  and its application to insect host-parasite systems.  Amer. Nat. 121:  244-54.   Templado,
  J.  1957.  Datos sobre Ooencyrtus
  kuwanai How. (Calcidido
  parásito de Lymantria dispar L.) en España.  Inst. Biol. Appl. Pub. 25: 
  119-29.   Tothill, J. D. 
  1916.  The introduction and
  establishment in Canada of the natural enemies of the brown-tail and gypsy
  moths.  Agric. Gaz.
  Canada 3:  111-16.   Versol, P.
  L. & W. G. Yendol.  1982. 
  Discrimination by the parasite, Apanteles
  melanoscelus, between
  healthy and virus-infected gypsy moth larvae.  Environ. Ent. 11: 
  42-45.   Webber, R. T.
  & J. V. Schaffner, Jr.  1926. 
  Host relations of Compsilura
  concinnata Meigen, an
  important tachinid parasite of the gypsy moth and the brown-tail moth.  U. S. Dept. Agric. Dept. Bull. 1363.  31 p.   Weseloh. R.
  & J. Anderson.  1975. 
  Inundative release of Apanteles
  melanoscelus against the
  gypsy moth.  Environ. Ent. 4:  33-36.   Weseloh, R. M., T. G. Andreadis, R. E. B.
  Moore, J. F. Anderson, N. R. Dubois & F. B. Lewis.  1983. 
  Field confirmation of a mechanism causing synergism between Bacillus thuringiensis and the gypsy moth parasitoid, Apanteles melanoscelus.  J.
  Invert. Path. 41:  99-103.   Wollam, J. D. & W. G. Yendol.  1976. 
  Evaluation of Bacillus
  thuringiensis and a
  parasitoid for suppression of the gypsy moth.  J. Econ. Ent. 69: 
  113-18.   |