FILE: <bc-36.htm>                                                                                                                       Pooled References                                GENERAL INDEX                                     [Navigate to   MAIN MENU ]
 
 
                     BIOLOGICAL
CONTROL OF ARTHROPODS IN GRAPES
                                                             (Contacts)
 
----Please CLICK on desired underlined categories [To search for Subject Matter, depress
Ctrl/F ]:
 
| Introduction            Vitis vinifera L.,
  the most widely cultivated species of grape, had been grown in Asia Minor between
  the Caspian and Black seas since the beginning of civilization (Winckler et
  al. 1974), flourishing especially in central Europe through the 14th Century.
  The invasion of grape phylloxera, Daktulosphaira
  vitifoliae (Fitch) from
  North America ca. 1886 markedly reduced the productive acreage in France, a
  plague that gradually spread to the Black Sea area within 10 years.
  Viticulturists were formed to develop resistant rootstocks and hybrid grapes
  that greatly sophisticated the industry (Gonzalez 1983).             In the some 10
  million hectares of grapes worldwide, hundreds of clonal selections and
  hybrids have been produced to adapt varieties to various climatic and soil
  conditions found on all continents (Gonzalez 1983). Such diverse viticulture
  modifies vine microclimates to favor or inhibit pests that are indigenous to
  the ecosystem of the grape plant. These various ecological niches created by
  the biocenosis of the vine are occupied in each grape region by different
  pests (Bournier 1976). As pest resistance to synthetic organic pesticides
  developed, there has been an interest in biological control (Flaherty et al.
  1985, Flaherty & Wilson 1999).    In a review of arthropod pests attacking grapes, Flaherty
  & Wilson (1999) consider major taxonomic groups as follows:     Cicadellidae.--There are nine species of leafhoppers that attack grapes
  (Bournier 1976). Erythroneura
  elegantula Osborn, the grape
  leafhopper, is the most common. Damage is caused by leaf chlorophyll reduction,
  vine defoliation, and damage of the surface of table grapes with excrement,
  and annoyance from leafhoppers to workmen (Jensen & Flaherty 1981a).    It was observed that grapes planted near streams and rivers,
  where wild blackberries, Rubus
  ursinus Chamisso &
  Schlecht and Rubus procerus Mueller, grow, do not
  sustain high grape leafhopper densities (Doutt & Nakata 1965, 1973).
  Principal reasons were the activity of Anagrus
  epos Girault parasitizing
  the eggs of both grape and blackberry leafhopper (Dikrella californica
  (Lawson)), a non economic species whose eggs are present year round on wild
  blackberries. This synchrony of blackberry leafhopper, grape leafhopper and A. epos phenology was reported by Williams (1984).   There was then considerable effort to establish effective
  blackberry refuges near commercial vineyards. However, successful control was
  not attained because overwintering numbers of A. epos
  were so few due to low D. californica egg production in
  winter (Flaherty et al. 1985). Effective overwintering of the parasitoid
  depended on continuous production of eggs by D. californica.
  Williams (1984) found a reproductive diapause in females of this species
  during winter. The importance of alternate host plants sustaining leafhoppers
  was reported by McKenzie & Beirne (1972), Kido et al. (1984) and Flaherty
  et al.(1985). Such host plants as apple, wild rose and French prune are
  important host plants for such leafhoppers. In the San Joaquin Valley of
  California, there is not an emphasis on the prune leafhopper, Edwardsiana prunicola (Edwards), as a major
  overwintering host of the parasitoid (Flaherty et al. 1985). Another species,
  Typhlocyba pomaria McAtee, on apple is
  also probably important.   Jensen & Flaherty (1981a) discuss how the parasitoid, A. epos importance varies with grape variety and its intended
  usage. High populations of grape leafhopper can be tolerated on Thompson
  Seedless grapes which are to be used for raisin or wine production, but only
  very low tolerance is on grapes grown for fresh market consumption. Spotting
  damage, which results from leafhopper feces, affects the value of the crop.
  On the table grape varieties Emperor and Ribier, the grape leafhopper
  populations increase to such high numbers even in the presence of the
  parasitoid, that control is unsatisfactory. Reasons for the parasitoid's
  greater effectiveness on Thompson Seedless are unknown, but some observations
  indicate that the smooth leaf surface of Thompson Seedless vines does not
  impede searching and oviposition of the parasitoid. Early maturing varieties
  also produce fewer newly mature leaves, sites which are favored by grape
  leafhopper for egg deposition. By comparison the later varieties such as
  Emperor and Ribier have tomentose (hairy) leaves that may interfere with the
  parasitoid. Leafhopper oviposition is also favored by the development of
  newly matured leaves late in the season. Later season irrigation in such
  vineyards also favors grape leafhopper (Jensen & Flaherty 1981a).   The parasitoid, Aphelopus
  albopictus Ashmead (= A. comesi Fenton) attacks all instars of the grape leafhopper
  (Cate 1975). Parasitoid eggs are placed between the nymph's 2nd and 3rd
  abdominal segments where they remain undeveloped until the nymph molts to the
  adult stage. The host appears normal during the parasitoid's larval
  development except for an elongating larval sack (the thylacium) that
  gradually protrudes from the abdomen with each parasitoid mold. By its 5th
  instar the parasitoid has developed mandibles and eviscerates the adult leafhopper.
  Prior to evisceration the adult leafhopper is functionally non-reproductive
  since gonads fail to develop in parasitized adults. Parasitism is usually
  between 10-40%, but Cate (1975) reported a high of 77%, and speculated that
  cultural practices might be altered to favor parasitism.   The variegated grape leafhopper, Erythroneura variabilis
  Beamer, is the principal vineyard pest in the lower Sonoran Desert of
  California, Arizona and Mexico. Infestations are severe in the Coachella
  Valley of California where the high temperatures allow for rapid development
  and as many as six generations per year (Barnes 1981). Activity of the
  parasitoid A. epos is low in this climate,
  becoming prominent only in the milder climates of the coastal plain where
  parasitism can reach 90% (Barnes 1981).   Variegated grape leafhopper invaded the San Joaquin Valley
  around 1980 and continues to spread. Defoliation occurs in Thompson Seedless
  vineyards especially where the grape leafhopper had been under good control
  by A. epos. The whole management strategy, built around the
  activity of this parasitoid, was altered with a renewed attention to chemical
  control. This caused outbreaks of secondary pests such as spider mites and
  mealybugs. The projected annual costs for control of variegated grape
  leafhopper were expected to be >$5-10 million, with yield and quality
  losses probably double that amount (Wilson et al. 1986, 1987).    Settle et al. (1986) commented "Variegated leafhopper is
  a more serious pest than the grape leafhopper, in part because of differences
  in egg-laying behavior. Variegated leafhopper eggs, deeply buried within the
  leaf tissue, are less likely to be detected by A. epos
  than grape leafhopper eggs, which stand out as blisters on the leaf
  surface."    A search for new parasitoids of variegated grape leafhopper
  was begun in 1985 in southern California, Arizona, Colorado, Texas, New
  Mexico and Mexico. The variety of species and biotypes of leafhopper
  parasitoids collected from diverse climatic zones and in different seasons were
  found (Gonzalez et al. 1988). It was found that A. epos
  had evolved a wide range of biotypes, differing in relative preference for
  the grape leafhopper and variegated grape leafhopper. Pickett et al. (1987)
  indicated that the San Joaquin Valley biotype had a 6.9X greater preference
  for grape leafhopper than for variegated grape leafhopper. On the basis of
  preference, biotypes from the Coachella Valley and Colorado would
  respectively choose, provided equal numbers of eggs of both hosts, 2-4.3
  times more variegated grape leafhopper eggs.    Erythroneura ziczac Walch
  is the most important insect on grapes in the Okanagan Valley, British
  Columbia (McKenzie & Beirne 1972). Two cultural procedures which
  prevented damage by leafhoppers were (1) destroying overwinter sites around
  the vineyards and (2) providing A.
  epos    Generalist predators, primarily spiders such as Theridion sp., may
  significantly impact leafhoppers in vineyards with cover crops (Settle et al.
  1986). In San Joaquin Valley studies, twice as many spiders were recorded in
  a vineyard with a weed cover crop. Settle et al. (1986) also found that
  Thompson seedless grapes grown on its own roots showed greatly reduced
  attractiveness to leafhoppers, resulting in a nearly 8X reduction in
  leafhopper numbers compared with the more vigorous vines on Saltcreek
  rootstock. Reduced leafhopper pressures afforded by cultural practices
  suggest a potential for biological control.                  Pierce’s Disease spread by sharpshooter leafhopper
  [Please refer to ch-120.htm]   Pseudococcidae.--Two mealybug species causing problems in California
  vineyards are the grape mealybug, Pseudococcus
  maritimus (Ehrhorn) and the
  obscure mealybug, Pseudococcus
  affinis (Mackell) (= P. obscurus Essig). The first species is principally a pest
  of table grape varieties whose bunches make contact with vine bark and become
  infested (Flaherty et al. 1981b). Before the late 1940's occasional losses
  occurred in table grapes, which were mostly spotty and generally
  nonproblematic. The problem gradually increased in the late 1940's with
  extensive use of DDT and other pesticides to control grape pests. The obscure
  mealybug, which has been recorded on a large number of hosts, was recently
  found to be a problem in unsprayed vineyards in San Luis Obispo County, a
  more coastal climate. The absence of effective parasitoids attacking obscure
  mealybug points to it as a recently introduced species that will require the
  importation of new natural enemies.   Clausen (1924) reported five primary endoparasitoids from
  grape mealybug in the central San Joaquin Valley, where late summer and
  autumn parasitism was >90% in 1919. Flaherty & Wilson (1999)
  reexamining Clausen's (1924) data concluded that Zarhopalus corvinus
  (Girault) was the most active. In the 1960's a ranking of host parasitism
  from samples of Doutt & Natata (unpublished) showed that Acerophagus notativentris (Girault) was the
  principal species, that Acerophagus
  subalbicornis (Girault) was
  occasionally found and that Z.
  corvinus was uncommon
  (Flaherty et al. 1976). Parasitoids were not reared from mealybug samples
  collected from an Emperor variety vineyard where heavy treatments. of
  pesticides were made.    Another mealybug, Maconellicoccus
  hirsutus (Green), is a pest
  of grape in India (Manjunath 1985). It attacks the varieties Thompson
  Seedless, Anab-e-Shahi and Bangalore Blue. Up to 90% of the clusters are
  destroyed, and chemical control is not effective. The encyrtid, Anagyrus dactylopii Howard, seems to offer some biological control
  potential. In late season samples at Bangalore, parasitization ranges from
  60-70%, although fields are regularly treated with insecticides. Manjunath
  (1985) recommended the introduction of Anagyrus
  kamali Moursi and Prochiloneurus sp. which
  reportedly give complete control of M.
  hirsutus in Egypt (Kamal
  1951).   Planococcus citri
  (Risso) damages >20 species of plants in the Soviet Union (Niyazov 1969).
  The parasitoid Anagyrus pseudococci (Girault) is active
  in the region, destroying up to 75% of the host populations in untreated
  areas. Allotropa mecrida (Walker) was
  responsible for 20% parasitism of P.
  citri in Turkemenia and
  Georgia. The encyrtids Leptomastidea
  abnormis (Girault) and Leptomastix dactylopii Howard were
  introduced into Georgia and Turkemia from the United States in 1960, but
  native hyperparasitoids reduced their effectiveness. In Transcaucasia and
  Soviet Central Asia, Thysanus
  (Chartocerus) subaeneus Forster was
  responsible for up to 20% hyperparasitism of A. mecrida.
  Rzaeva (1985) reported that L.
  abnormis successfully
  established on Planococcus ficus Signoret, a mealybug pest
  of grapes in eastern Transcaucasus. The introduction of Clausenia josefi
  Rosen also was recommended (Niyazov 1969), as well as A. notativentris
  from California.   The effectiveness of predators in California vineyards is
  generally unknown. Mealybug egg masses have been attacked by cecidomyiid fly
  larvae (Flaherty et al. 1982). Adults of Chrysoperla
  spp. (= Chrysopa spp.) are
  often abundant on grapevines with mealybugs, adults being attracted to
  mealybug honeydew. Cryptolaemus
  montrouzieri Mulsant (the
  mealybug destroyer) is rare in California vineyards. The use of this predator
  for mealybug control in the Soviet Union was reviewed by Yanosh &
  Mjavanadze (1983). Cryptolaemus
  was particularly effective on Chloropulvinaria
  floccifera Westwood on tea,
  with adult beetles being field released. Niyazov (1969) reported that one of the
  most effective predators of mealybugs on grape in the Soviet Union was C. montrouzieri which had been introduced from Egypt in 1932.
  Other coccinellids of importance in Turkemenia were Coccinella spetempunctata
  L., Scymnus apetzi Mulzant, Hyperaspis polita Weise, Scymnus
  subvileosus (Goeze), Nephus bipunctatus Kugelann and Scymnus biguttatus
  Mulsant. Larvae of Leucopis
  (Leucopomya) alticeps Czerny and Chrysoperla carnea (Stephens) were active
  on all mealybug stages. The coccinellids were parasitized by Homalotylus sp. and the
  chrysopids by Telenomus acrobates Girard.   Coccidae.--Gonzalez
  (1983) reported that grape quality can be affected by copious amounts of
  honeydew produced by Parthenolecanium
  persicae (F.) in Chile, but
  natural enemies are important in minimizing damage. The principal parasitoids
  were Coccophagus caridei (Brethes) and Metaphycus flavus (Howard). These and other parasitoids were common
  natural enemies of lecanium coccids on other plants including P. corni (Bouché) which is also a pest of grapes in Chile.    Phylloxeridae.--The coccinellid Scymnus
  cervicalis Mulsant is the
  only natural enemy considered important as a predator of the leaf-feeding
  form of grape phylloxers, D.
  vitifoliae, on wild grapes
  in Erie County, Pennsylvania (Wheeler & Jubb 1979).    Tetranychidae.--Spider mites became serious grape pests after World War II,
  at the same time that synthetic organic insecticides appeared (Flaherty et
  al. 1985). Two spider mite species which are commonly found on California
  grapes are the Pacific spider mite, Tetranychus
  pacificus McGregor, and the
  Willamette spider mite, Eotetranychus
  willamettei (Ewing)
  (Flaherty et al. 1981a). Two-spotted spider mite, T. uriticae
  Koch. is rare on grapes in California.   In the eastern United States, European red mite, Panonychus ulmi (Koch), is the principal spider mite problem (Jubb et
  al. 1985). This species is also a pest in Europe. Schruft (1986) listed E. carpini vitis
  Boisduval, T. urticae, T. mcdanieli
  McGregor and T. turkestani Ugarov &
  Nikolski also as pests in Europe. Oligonychus
  vitis Zaher & Shehata
  was reported serious on grapes in Egypt and Chile (Rizk et al. 1978, Gonzalez
  1983). In the Soviet Union spider mite pests are P. ulmi, Eotetranychus pruni (Oudemans), T. turkestani and Bryobia
  praetiosa Koch . Schruft
  (1986) reported that E. pruni is important as a pest in
  Bulgaria. In India there are four species, Oligonychus. mangiferus
  (Rahman & Sapra), O. punicae (Hirst), T. urticae, and E.
  truncatus Estebanes &
  Baker (Schruft 1986). In Japan grapes are hosts for B. praetiosa,
  E. smithi Pritchard & Baker, T. kanzawai
  Kishida and T. urticae (Schruft 1986).   In San Joaquin Valley, California vineyards, the most
  important natural enemy of spider mites us the predatory mite Metaseiulus occidentalis (Nesbitt)
  (Flaherty et al. 1981a). Amblyseius
  californicus (McGregor) is
  important in the Salinas Valley and M.
  mcgregori (Chant) in the
  Sacramento Valley. Although these predators prey on the Willamette spider
  mite, their effectiveness is unknown. In the eastern United States the most
  common predatory mites on Concord grapes (Vitis
  labrusca L.) are the
  phytoseiids, Neoseiulus (Amblyseius) fallacis (Garman) and Amblyseius andersoni (Chant), and the stigmaeid Zetzellia mali
  (Ewing). Neoseiulus fallacis and Z. mali may be important in natural control of P. ulmi (Jubb et al. 1985). In Europe the cost common
  phytoseiids are Typhlodromus
  pyri Scheuten, Euseius (Amblyseius) finalndicus
  (Oudemans), Amblyseius aberrans (Oudemans) and A. andersoni, but only T.
  pyri is of importance in
  biological control (Schruft 1986). However, A. aberrans
  is very important in Italy (Gambaro 1972). Rizk et al. (1978) reported that Agistemus
  exsertus Gonzalez, Amblyseius gossipi El-Badry and Tydeus
  californicus (Banks) are
  very abundant in middle Egypt, while in Chile Amblyseius chilenensis
  (Dosse) is very important (Gonzalez 1983).   Spider mite control
  can be somewhat predicted by the ratio of the number of predators to
  spider mites. For any system there exists a particular predator/prey ratio at
  which the pest population will be controlled. For example, Tanigoshi et al.
  (1983) reported that a 1:10 ratio of Neoseiulus
  fallacis to P. ulmi provided control in Red Delicious apples. In another
  orchard with a different apple variety, Tanigoshi et al. (1983) found a 1:20
  ratio was sufficient, and indicated that relatively fewer predaceous mites
  were required to provide control as a result of reduced spider mite fecundity
  on this variety. Wilson et al. (1984)
  found that a 1:11 ratio of Metaseiulus
  occidentalis to Tetranychus spp. provided
  control in almonds within two weeks when the spider mites were at densities
  of >5 mites per leaf. At lower densities an increasingly higher
  predator/prey ratio was required.   It is very tedious to estimate spider mite abundance and
  predator effectiveness, because mites are extremely small, and often
  numerous. Schruft (1986) found that it is possible to estimate the risk of
  damage by P. ulmi or E. carpini
  vitis using a method developed
  by Baillod et al. (1979). The method tests the relationship between the
  number of spider mites per leaf and the proportion of leaves in a sample
  occupied by mites. Therefore, instead of counting the mites themselves, the
  number of leaves with one or more mites is recorded. The same sampling
  procedure has been used to evaluate predaceous mites (Baillod & Venturi
  1980). Flaherty et al. (1981a) used an infested leaf (binomial) predator/prey
  ratio, together with information on the relative level of spider mites in the
  vineyard. Based on observations over several years, they found that a 1:2
  (0.5) binomial ratio of predator to spider mite infested leaves was
  sufficient for control. This ratio was less conservative than the ratios
  derived using the Wilson et al. (1984) procedure for almonds. A binomial
  ratio of ca. 1:1 is equivalent to a 1:10 count ratio at densities between
  15-50 spider mites per leaf. A binomial ratio closer to that reported by
  Flaherty et al. (1981a) was calculated when using a 1:20 count ratio . The
  lower ratio for grapes may indicate a lowered reproductive capacity for
  spider mites on grapes compared to that found on almonds, or perhaps for that
  found by Tanigoshi et al. (1983) on apples.   Alternate foods of predaceous mites have been considered in predator/prey
  relations. Flaherty (1969) reported that M.
  occidentalis was better able
  to regulate low densities of Willamette mites in the presence of small number
  of T. urticae that moved from weeds onto grape leaves. Flaherty et
  al. (1981a) recommended that Willamette spider mite be considered as an
  important alternate prey because it is a much less serious pest of grapes
  than Pacific spider mite. Metaseiulus
  occidentalis also preys on
  other mites, such as tydeids, eriophyids and perhaps tarsonemids. In Europe
  additional food for T. pyri includes eriophyids,
  tydeids, pollen and pearls of the grape (Schruft 1972). The possible benefits
  of augmenting pollen feeding tydeids by pollen applications or planting cover
  crops that produce wind borne pollen exists (Flaherty & Hoy 1971, Calvert
  & Huffaker 1974). Gambaro (1972) reported that Amblyseius aberrans
  was able to live and reproduce in the absence of prey and thus could maintain
  spider mite populations at low densities.   Viticultural practices influence spider mite outbreaks (Flaherty et al. 1981a).
  Emphasis is placed on avoiding problems associated with low vine vigor, dusty
  conditions and water stress, which can greatly increase the chance of Pacific
  spider mite outbreaks. Although 10 species of phytoseiid mites are known in
  commercial vineyards of the San Joaquin Valley, only M. occidentalis
  seems to pay a significant role in natural control of spider mites (Flaherty
  & Huffaker 1970). The predaceous mite Amblyseius
  nr. hibisci becomes abundant
  where triadimefon replaced sulfur for control of powdery mildew, Uncinula necator Burrill. The predaceous mite is common in wild
  grapes where sulfur is not applied (Flaherty et al. 1985). English-Loeb et
  al. (1986) showed that A.
  nr. hibisci was not only the
  dominant phytoseiid species where sulfur was not applied but it also
  maintained lower numbers of Willamette spider mites than M. occidentalis
  where sulfur was used. The phytoseiid Typhloseiopsis
  smithi (Schuster) was also
  recorded on non sulfur treated grape foliage (English-Loeb et al. 1986).   Arthropod predators, such as predaceous insects and spiders, are considered as
  ineffective natural enemies of spider mites (Flaherty et al. 1981a), because
  they appear too late in the season or increase in numbers too slowly.
  However, their contribution to natural control in vineyards might be
  significant. Sometimes six-spotted thrips, Scolothrips sexmaculatus
  (Pergande) destroys Pacific spider mite populations. This predator is
  unpredictable, however, which may be related to periodic low prey densities.
  In Italy anthocorids and coccinellids are considered effective at high prey
  densities (Duso & Girolami 1985). Schruft (1986) reported that predaceous
  insects, Scymnus sp., Oligota sp., Scolothrips longicornis Priesner, Anthocoris nemorum (L.) and Orius
  minutus (L.) are found on
  grapes infested with P. ulmi, but their importance for
  biological control of red spider mite populations is unknown. However, it is
  certain that some chrysopids, particularly Chrysoperla carnea,
  are effective predators of red spider mites during summer and late autumn
  (Schruft 1986).   Spider mite control by insect predators may be subtle as well
  as important, because observations in vineyards and laboratory studies
  revealed that western flower thrips, Frankliniella
  occidentalis (Pergande)
  which is a pest of grapes, feeds on Pacific spider mite eggs and may actually
  affect the pest's population in vineyards (Flaherty et al. 1981a). Franklineilla occidentalis predation is apparently
  also important in cotton on spider mites (Gonzalez et al. 1982, Gonzalez
  & Wilson 1982, Trichilo 1986).   Mass releases of M.
  occidentalis for control of
  Pacific spider mites are not practical (Flaherty et al. 1985), but an autumn
  release program may be more useful. Flaherty & Huffaker (1970) showed
  that late season predator activity in vineyards is essential to spider mite
  balance. A fall release of M.
  occidentalis resulted in
  excellent biological control of Willamette spider mite the following spring
  and summer. Hoy & Flaherty (1970, 1975) considered late season diapause
  induction important for the successful overwintering of M. occodentalis
  populations. Flaherty et al. (1985) thought that a fall release of predators
  reared under diapausing conditions would minimize the timing and survivorship
  problems associated with early summer releases because immediate control of
  Pacific spider mite in the fall is not a factor and diapausing predators
  require little food. In Italy, Girolami & Duso (1985) reported on the
  establishment of predator/prey equilibrium in pesticide-disturbed vineyards
  with reintroductions of A. aberrans. Baillod et al. (1982) described methods for reintroduction of T. pyri into vineyards in Switzerland and recommended their
  use for biological control of phytophagous mites. Schruft (1986) reported the
  artificial release of T. pyri by the introduction of
  infested canes or foliage.   Tenuipalpidae.--Brevipalpus
  chilensis Baker is serious
  on grapes in Chile, which developed as a consequence of indiscriminate use of
  pesticides (Gonzalez 1983). Important to consider preserving is the
  predaceous mite A. chilenensis. In Victoria,
  Australia, B. lewisi McGregor causes a
  superficial scaring of bunch and berry stems (Buchanan et al. 1980). A close relationship
  between B. lewisi and its most common
  phytoseiid predator Amblyseius
  reticulatus (Oudemans) did
  not reveal regulation of B. lewisi numbers by A. reticulatus during the growing season. However, large
  numbers of A. reticulatus during the end of the
  growing season may reduce the number of B.
  lewisi that can overwinter.
  The false spider mite Tenuipalpus
  granati Sayed has been
  considered a serious pest of grapes in Egypt (Rizk et al. 1978), which was
  blamed mostly on pesticide upsets. The predators Agistemum exsertus,
  Amblyseius gossipi and Tydeus californicus were observed to be associated with T. granati.   Eriophyidae.--The eriophyid mite Colomerus
  vitis (Pagenstecher) attacks
  various species and hybrids of grapes. Different biotypes of the eriophyid
  have been found in California, separated by injury type (Kido 1981). The
  phytoseiid mite M. occidentalis was reported
  effective in reducing populations of C.
  vitis. Schruft (1972) reported
  that C. vitis and Calepitrimerus
  vitis (Nalepa) also
  eriophyid pests in Europe, were destroyed by the tydeids Tydeus götzi
  Schruft and Pronematus stärki Schruft.     Tortricidae.--Grape clusters are often attacked by tortricids worldwide.
  The orange tortrix, Argyrotaenia
  citrana (Fernald), is a
  major pest in cooler coastal regions of California. Larvae cause damage by
  feeding in grape clusters and permitting rots to invade (Kido et al. 1981c). Kido et al. (1981b) assessing biological control sampled Gamay Beaujolais
  vines in Salinas Valley vineyards. One vineyard (Soledad) had a history of
  injurious infestations that required treatments. The other (Greenfield) had
  very light infestations and no treatments were required. Samples of clusters
  from the Greenfield vineyard contained few orange tortrix larvae and pupae,
  with 53.5% parasitism, while the Soledad vineyard with a high orange tortrix
  density had 16% parasitism. Exochus
  nigripalpus subobscurus Townes was the
  predominant parasitoid in both vineyards. Apanteles
  aristoteliae Viereck was
  less frequent.   The coyote brush, Baccharis
  pilularis DeCandolle also
  sustained orange tortrix infestations. Large numbers of another tortricid
  species Aristoteliae argentifera Busck were found on
  coyote brush located near the Greenfield vineyard and several parasitoids
  were recovered from larvae and pupae (Exochus
  sp. and Apanteles sp.).
  Coyote brush was much less abundant near the Soledad vineyard and consisted
  mainly of young plants and no infestation of A. argentifera.   The omnivorous leafroller, Platynota
  stultana Walsingham, has
  become a major pest in the warmer inland valleys of California since 1960
  (Kido et al. 1981a). It causes a rot similar to that of the orange tortrix. A
  number of insect parasitoids have been recorded on omnivorous leafroller in
  vineyards, but parasitoids seldom accounted for >10% mortality even on
  very high worm infestations. Flaherty et al. (1985) recommended the importation
  and augmentation of natural enemies of this insect in the San Joaquin Valley.   Trichogramma spp. have been mass released to augment biological control of
  omnivorous leafroller and orange tortrix. Makhmudov et al. (1977) reported
  that Trichogramma sp.
  releases gave good control of Lobesia
  botrana (Schiff), a
  tortricid attacking grapes in the Soviet Union. Marcelin (1985) reported
  significant reductions of L.
  botrana and Eupoecilia ambiguella (Hübner) populations with Trichogramma sp. releases. The selective control of
  tortricids in grapes with Bacillus
  thuringiensis Berliner and
  mating disruption has been stressed in Europe.   Damage by Proeulia
  auraria (Clarke) was
  reported from Chile by Gonzalez (1983) when natural enemies were destroyed by
  pesticides. A complex of five species of egg and larval parasitoids are
  associated with this pest. The encyrtid, Encarsia
  sp. attacked eggs. Larval parasitoids included eulophids Elachertus and Bryopezus,
  a braconid Apanteles, and
  unidentified ichneumonid, and a tachinid, Ollacheryphe
  aenea (Aldrich).    The western grapeleaf skeletonizer, Harrisina brillians
  Barnes & McDunnough, was originally distributed throughout the
  southwestern United States and northern Mexico. It was first found in
  California in San Diego in 1941, where it severely defoliated wild grapes, Vitis girdiana Munson in the canyons. Soon it became a serious
  pests in commercial vineyards. The larvae are voracious feeders and can
  devastate a crop by defoliating an entire vineyard.   In 1950 efforts were initiated in the University of California
  to control grapeleaf skeletonizer biologically. Parasitoids were introduced,
  with two species, the braconid, Apanteles
  harrisinae Muesebeck and the
  tachinid, Ametadoria miscella (Wulp) (= Sturmia harrisinae Coquillett) predominating (Clausen 1961). A
  virulent granulosis virus was also accidentally introduced.    Surveys in San Diego County in 1982-1983 revealed that it was
  necessary to spray grapeleaf skeletonizer in commercial vineyards (Flaherty
  et al. 1985). Abandoned untreated vineyards and backyard vines were severely
  defoliated despite the activity of the imported parasitoids. Symptoms of
  virus infection were not observed in the survey. Grapeleaf skeletonizer was
  not found in wild grapes, V.
  girdiana, except where they
  were in close proximity to heavily infested commercial V. vinifera
  vineyards.   The skeletonizer invaded the San Joaquin Valley in 1961
  (Clausen 1961), and new infestations appeared thereafter throughout the
  Central Valley in spite of eradication efforts. Renewed efforts to introduce
  natural enemies were made in the 1980's, which resulted in the translocation
  of parasitoids from southern California and the acquisition of new species
  and strains from Torreón vicinity in Mexico (E. F. Legner and B. Villegas,
  unpub. data). Extensive insecticide treatment during introduction, however,
  precluded establishment in most areas. Some success was achieved outside the
  principal grape production area near Redding, with the establishment of Apanteles spp. and Ametadoria spp. This insect is
  now regarded a serious pest of commercial vineyards and backyard vines, as
  well as in wild grapes, Vitis
  californica Bentham. Apanteles harrisinae and A.
  miscella were not
  successfully established in the San Joaquin Valley (Flaherty et al. 1985).
  Only a few parasitoid recoveries were made at release sites which may be
  related to heavy spray pressure during the introduction period (E. F. Legner,
  unpub. data). Samples of larvae taken from heavily infested and abandoned vineyards
  in San Diego County showed only 13% parasitism, which is below the 42-62%
  reported by Clausen in 1953-54 (Clausen 1961). There was also no evidence of
  virus present. Clausen (1961) thought that the virus must be credited with
  the major role in reducing grapeleaf skeletonizer populations to low levels
  and exterminating many small infestations. Flaherty et al. (1985) considered
  that at that time the virus was more widespread and had reduced grapeleaf
  skeletonizer populations to levels that made it more manageable by the
  parasitoids. This may account for the greater parasitism reported by Clausen
  (1961) and that found by Flaherty et al. (1985). However, the present absence
  of virus in abandoned vineyards in San Diego County and the absence of
  observable grapeleaf skeletonizer in wild grapes is considered an enigma. The
  grapeleaf skeletonizer has been known to show cyclic abundance, however, and
  the surveys conducted in San Diego County could have been during one of the
  cyclic outbreaks. Surveys by Legner (unpub. data) during other years have
  shown this insect to be as rare as reported by Clausen earlier. Also,
  widespread application of insecticides to vineyards in the south could be
  responsible for minimizing natural enemy activity. In the San Joaquin Valley
  the virus of grapeleaf skeletonizer is extremely virulent and has the
  potential of becoming incorporated into an areawide biological control
  effort, including wild grapes, backyard vines and commercial vineyards
  (Flaherty et al. 1985).   Pyralidae.--The grape leaffolder, Desmia
  funeralis (Hübner), is a
  pest of grapes in the central and southern San Joaquin Valley. The larvae
  rolling and feeding on the leaves cause injury. Some feeding on fruit occurs
  at high densities, but economic damage usually occurs only with massive, late
  season infestations (Jensen & Flaherty 1981b). The larval parasitoid Bracon cushmani (Muesebeck) commonly attacks grape leaffolder.
  Parasitism ranges from 30-40% and higher. Bracon
  cushmani usually increases
  in summer and frequently reduces the size of the second and third brood to
  such small numbers that little increase in host populations is detectable
  (Jensen & Flaherty 1981b).   Sesiidae.--The
  grape root borer, Vitacea polistiformis (Harris) is a
  pest of grapes east of the Rocky Mountains. Larvae prune and girdle grape
  roots by excavating irregular burrows (Jubb 1982). Saunders & All (1985)
  showed an inverse correlation between the severity of V. polistiformis
  and the activity of entomophilic rhabditoid nematodes in vineyard soils.
  Laboratory and field bioassays determined the susceptibility of 1st instar
  larvae to the nematode Steinernema
  feltiae Filipjev, and the
  insect nematode interaction was considered a type of natural control on
  larvae. Augmentation of entomophilic rhabditoid nematodes during the critical
  period of oviposition and eclosion was suggested as a technique for control.     Curculionidae.--Adults of Naupactus
  xanthographus (Germar)
  consume grape buds and leaves in Chile (Gonzalez 1983). Damage also occurs when
  feces adheres to foliage and fruit clusters. Combined damage by adult and
  larval feeding on root-weakened vines. A complex of pathogens (bacteria,
  fungi), nematodes and insects attack larvae and pupae in the soil. A nematode
  of the family Rhabditidae parasitizes 4th-5th instars. The same nematode
  attacks other Coleoptera and can be reared on wax moth larvae, Galleria melonella (L.). Gonzalez (1983) reported that larvae are
  often attacked by nematodes that are transported in irrigation water, but the
  degree of control was not evaluated. Of importance as a natural enemy is Platystasius sp (Fidiobia sp.). Up to 60% of the
  egg masses under the bark can be attacked. Gonzalez (1983) reported that its
  action in conjunction with the complex of other natural enemies is sufficient
  to keep N. xanthographus below the
  economic threshold.   Otiorhynchus sulcatus
  (F.), the black vine weevil, is important in horticultural crops in Europe,
  the United States, Canada, Australia and New Zealand. Adults seriously damage
  berry pedicels and cluster stems and larvae feed on roots in Europe and
  central Washington (Bedding & Miller 1981). The application of aqueous
  suspensions of infective juvenile Heterorhabditis
  heliothidis (Khan, Brooks
  & Hirschmann) to the soil resulted in up to 100% parasitism of larvae of O. sulcatus in potted grapes in nurseries. Pupae and newly
  emerged adults were also parasitized. Steinernema
  bibionis (Bovien) was found
  less effective.    Bostrichidae.--Medalgus confertus (LeConte), a branch
  and twig borer, is found in California associated with many species of
  cultivated and native trees and shrubs. In grapes both adult and larval
  stages cause injury to grapevines (Joos 1981). Little is known about the
  natural enemies of M. confertus, but a neuropteran
  predator in the Rhaphidiidae, and two coleopterans in the families Carabidae
  and Ostomidae may be very active. Recent studies have shown that the
  entomophagous nematode, S. feltiae, can move through frass
  tubes to infect larvae.     Thripidae.--Several species of thrips, such as Frankliniella spp. and Drepanothrips
  reuteri Uzel, can be
  pestiferous on grapes worldwide (Flaherty & Wilson 1988). Jensen et al. (1981) report that little is known about their natural control
  in California, however. Some studies in California citrus show that
  phytoseiid mites Euseius tularensis Cugdon can control
  the citrus thrips Scirtothrips
  citri (Moulton). Schwartz
  (1987) reported that Amblyseius
  citri van der Merwe &
  Ryke preyed on Scirtothrips aurantii Faure in South Africa.
  Schwartz (1987) also found that Amblyseius
  addoensis van der Merwe
  & Ryke most likely preyed on Thrips
  tabaci Lindemann in South
  African table grapes, although it was not sufficiently effective during mid
  summer.     REFERENCES:         [Additional references may
  be found at  MELVYL Library ]   Baillod, M., J. P. Bassino & P. Piganeau. 1979.
  L'estimation du risque provoqué par l'acarien rouge (Panonychus ulmi
  Koch) et l'acarien des charmilles (Eotetranychus
  carpini Oud.) en
  viticulture. Revue
  Suisse Vitic. Arboric. Hortic. 11:
  123-30.   Baillod, M., A. Schmid, E. Guignard, P. Antonin & R.
  Caccia. 1982.
  Lutte biologique contre l'acarien rouge en viticulture. II. Equilibres
  naturels, dynamique des populations et expériences de lachers de
  typhlodromes. Revue Suisse Vitic. Arboric.
  Hortic. 14: 345-52.   Baillod, M. & I. Venturi. 1980. Lutte biologique contre
  l'acarien rouge en viticulture. I.
  Répartition, distribution et métode de controle des populations de prédateurs
  typhlodromes. Rev. Suisse Vitic. Arboric. Hortic. 12: 231-38.   Barnes, M. M. 1981. Variegated grape leafhopper of southern
  California. p. 137-39. In:
  D. L. Flaherty, F. L. Jensen, A. N. Kasimatis, H. Kido, & W. J. Moller
  (eds.), Grape Pest Management. Univ. Calif., Berkeley, Agric. Sci. Publ.
  4105. 312 p.   Bedding, R. A. & L. A. Miller. 1981. Use of a nematode, Heterorhabditis heliothidis, to control black
  vine weevil, Otiorhynchus sulcatus, in potted plants.
  Ann. Appl. Biol. 99: 211-16.   Bellows, T. S., Jr. & T. W. Fisher, (eds) 1999. Handbook
  of Biological Control: Principles and Applications. Academic Press, San
  Diego, CA.  1046 p.   Bournier, A. 1976. Grape insects. Ann. Rev. Ent. 22: 355-76.   Buchanan, G. A., M. Bengston & E. M. Exley. 1980.
  Population growth of Brevipalpus
  lewisi McGregor (Acarina:
  Tenuipalpidae) on grapevines. Aust. J. Agric. Res. 31: 957-65.   Calvert, D. J. & C. B. Huffaker. 1974. Predator (Metaseiulus
  occidentalis) - prey (Pronematus spp.) interactions
  under sulfur and cattail pollen applications in a non-commercial vineyard. Entomophaga 19: 361-69.   Cate, J. R. 1975. Ecology of Erythroneura
  elegantula Osborn
  (Homoptera: Cicadellidae) in grape agroecosystems in California. Ph.D.
  dissertation, Univ. of California, Berkeley.   Clausen, C. P. 1924. The parasites of Pseudococcus
  maritimus (Ehrhorn) in
  California (Hymenoptera, Chalcidoidea). Part II. Biological studies and life
  histories. Univ. Calif. Publ. Ent. 3: 253-88.   Clausen, C. P. 1961. Biological control of western grape leaf skeletonizer (Harrisina brillians B. & McD.) in California. Hilgardia 31:
  613-37.   Daane, K. M., D. Gonzalez, D. L. Flaherty, H. Andris, G.
  Leavitt & W. Bentley. 1990a. Biological control of the variegated
  leafhopper: II. Field Evaluation. Calif. Table Grape Comm. & Calif.
  Raisin Adv. Bd., Ann. Crop. Rept. 1989.   Daane, K. M., D. Gonzalez, D. L. Flaherty, G. Y. Yokota &
  R. F. Gill. 1990b. New Anagrus
  epos biotypes for variegated
  leafhopper control in California. 74th Ann. Meet., Pacific Br. Ent. Soc. Amer., Spokane, WA.   Doutt, R. L. & J. Nakata. 1965. Overwintering refuge of Anagrus epos
  (Hymenoptera: Mymaridae). J.
  Econ. Ent. 58: 586.   Doutt, R. L. & J. Nakata. 1973. The Rubus
  leafhopper and its egg parasitoid: An endemic biotic system useful in
  grape-pest management. Environ.
  Ent. 2: 381-86.   Duso, C. & V. Girolami. 1985.
  Strategie di controllo biologico degli acari tetranichidi su vite. Atti XIV Congr. naz. Ital. Ent., Palermo, Erice, Bagheria. p.
  719-28.   English-Loeb, G. M., D. L. Flaherty, L. T. Wilson, W. W.
  Barnett, G. M. Leavitt & W. H. Settle. 1986. Pest management changes
  affect spider mites in vineyards. Calif. Agric. 40: 28-30.   Flaherty, D. L. 1969. Ecosystem trophic complexity and
  Willamette mite, Eotetranychus
  willamettei Ewing (Acarina:
  Tetranychidae), densities. Ecology 50: 911-16.   Flaherty, D. L. & M. A. Hoy. 1971. Biological control of
  Pacific mites and Willamette mites in San Joaquin Valley vineyards: Part III.
  Role of tydeid mites. Res.
  Popul. Ecol. 8: 80-96.   Flaherty, D. L. & C. B. Huffaker. 1970. Biological control
  of Pacific mites and Willamette mites in San Joaquin Valley vineyards. I.
  Role of Metaseiulus occidentalis. II. Influence of
  dispersion patterns of Metaseiulus
  occidentalis. Hilgardia 40:
  267-330.   Flaherty, D. L. & L. T. Wilson. 1999. Biological control
  of insects and mites on grapes. In
  Fisher, T. W. & T. S. Bellows, Jr. (eds) 1999. Handbook of Biological
  Control: Principles and Applications. Academic Press, San Diego, CA   Flaherty, D. L., M. A. Hoy & C. D. Lynn. 1981a. Spider
  mites. p. 111-25. In: D. L.
  Flaherty, F. L. Jensen, A. N. Kasimatis, H. Kido, & W. J. Moller (eds.),
  Grape Pest Management. Univ. Calif., Berkeley, Agric. Sci. Publ. 4105. 312 p.   Flaherty, D., F. Jensen & J. Nakata. 1976. Grape mealybug. Grape pest management in the southern
  San Joaquin Valley. San
  Joaquin Valley Agr. Res. Ext. Center
  Publ. 13 p.   Flaherty, D. L., F. L. Jensen, W. L. Peacock & L. Bettiga.
  1981b. Grape mealybug. p. 160-64. In: D. L. Flaherty, F. L. Jensen, A. N.
  Kasimatis, H.    Kido, & W. J. Moller (eds.), Grape Pest Management. Univ.
  Calif., Berkeley, Agric. Sci. Publ. 4105. 312 p.   Flaherty, D. L., W. L. Peacock, L. Bettiga & G. M.
  Leavitt. 1982. Chemicals losing effect against grape mealybug. Calif. Agric.
  36: 15-16.   Flaherty, D. L., L. T. Wilson, V. M. Stern & H. Kido.
  1985. Biological control in San Joaquin Valley vineyards. p. 501-20. In: M. A. Hoy & D. C.
  Herzog (eds.), Biological Control in Agricultural IPM Systems. Academic
  Press. 589 p.   Gambaro, P. I. 1972. Il ruolo del Typhlodromus aberrans Oudm. (Acarina,
  Phytoseiidae) nel controllo biologico degli Acari fitofagi dei vigneti del
  Vernonese. Boll.
  di Zool. Agraria
  e di Bachictura Ser. 11: 151-65.   Girolami, V. & C. Duso. 1985.
  Controllo biologico degli acari nei vigneti. L'Informatore Agrario 41: 83-9. Gonzalez, D. & L. T. Wilson. 1982. A food-web approach to economic thresholds: A sequence
  of pests and predaceous arthropods on California cotton. Entomophaga 27:
  31-43.   Gonzalez, D., B. R. Patterson, T. F. Leigh & L. T. Wilson.
  1982. Mites: A primary food source for two predators in San Joaquin Valley
  cotton. Calif. Agric. 36: 18-20.   Gonzalez, D., W. White, C. Pickett, V. Cervenka, M. Moratorio
  & L. T. Wilson. 1988. Biological control of variegated leafhopper in
  grape IPM program. Calif. Agric. 42: 23-5.   Gonzalez, D., K. M. Daane & D. L.
  Flaherty. 1990. Biological
  control of the variegated leafhopper: I. Insectary Production. Calif. Table
  Grape Comm. & Calif. Raisin Advisory Bd., Ann. Crop Rept. 1989.   Gonzalez, R. H. 1983. Manejo de plagas
  de la vid. Ciencias Agri. 13, Univ. de Chile. 115 p.   Hoy, M. A. & D. L. Flaherty. 1970. Photoperiodic induction
  of diapause in a predaceous mite, Metaseiulus
  occidentalis. Ann. Ent. Soc. Amer. 63: 960-63.   Hoy, M. A. & D. L. Flaherty. 1975. Diapause induction and
  duration in vineyard-collected Metaseiulus
  occidentalis. Environ. Ent. 4: 262-64.   Jensen, F. L. & D. L. Flaherty. 1981a. Grape leafhopper. p. 98-110. In: D. L. Flaherty, F. L. Jensen, A. N. Kasimatis, H.
  Kido, & W. J. Moller (eds.), Grape Pest Management. Univ. Calif.,
  Berkeley, Agric. Sci. Publ. 4105. 312 p.   Jensen, F. L. & D. L. Flaherty. 1981b. Grape leafroller. p. 147-54. In: D. L. Flaherty, F. L. Jensen, A. N. Kasimatis, H.
  Kido, & W. J. Moller (eds.), Grape Pest Management. Univ. Calif.,
  Berkeley, Agric. Sci. Publ. 4105. 312 p.   Jensen, F. L., D. L. Flaherty & D. A.
  Luvisi. 1981. Thrips. p. 176-88. In:
  D. L. Flaherty, F. L. Jensen, A. N. Kasimatis, H. Kido, & W. J. Moller
  (eds.), Grape Pest Management. Univ.
  Calif., Berkeley, Agric. Sci. Publ. 4105. 312 p.   Joos, J. L. 1981. Branch and twig borer. p. 201-02. In: D. L. Flaherty, F. L.
  Jensen, A. N. Kasimatis, H. Kido, & W. J. Moller (eds.), Grape Pest
  Management. Univ. Calif., Berkeley, Agric. Sci. Publ. 4105. 312 p.   Jubb, G. L., Jr. 1982. Occurrence of the grape root borer Vitacea polistiformis, in Pennsylvania. Melsheimer Ent. Ser. 32: 20-4.   Jubb, G. L., Jr., E. C. Masteller &
  R. D. Lehman. 1985. Survey of
  arthropods in vineyards of Erie County, Pennsylvania. Acari. Intl. J. Acarol. 11: 201-08.   Kamal, M. 1951. Biological control projects in Egypt, with a
  list of introduced parasites and predators. Bull. Soc. Fouad ler Ent. 35:
  205-20.   Kido, H. 1981. Grape erineum mite. p. 217-20. In: D. L. Flaherty, F. L.
  Jensen, A. N. Kasimatis, H. Kido, & W. J. Moller (eds.), Grape Pest
  Management. Univ. Calif., Berkeley, Agric. Sci. Publ. 4105. 312 p.   Kido, H., D. L. Flaherty, W. W. Barnett & H. L. Andris.
  1981a. Omnivorous leafroller. p. 126-36. In: D. L. Flaherty, F. L. Jensen, A. N.
  Kasimatis, H.    Kido, & W. J. Moller (eds.), Grape Pest Management. Univ.
  Calif., Berkeley, Agric. Sci. Publ. 4105. 312 p.   Kido, H., D. L. Flaherty, D. F. Bosch & K. A. Valero.
  1984. French prune trees as overwintering sites for grape leafhopper egg
  parasite. Amer. J. Enol. Vitic. 35: 156-60.   Kido, H., D. L. Flaherty, C. E. Kennett, N. F. McCalley &
  D. F. Bosch. 1981b. Seeking the reasons for differences in orange tortrix
  infestations. Calif. Agric. 35: 27-8.   Kido, H., N. F. McCalley & J. L. Joos. 1981c. Orange
  tortrix. p. 155-59. In: D.
  L. Flaherty, F. L. Jensen, A. N. Kasimatis, H. Kido, & W. J. Moller
  (eds.), Grape Pest Management. Univ. Calif., Berkeley, Agric. Sci. Publ.
  4105. 312 p.   Makhmudov, D., A. Azimov, A. Z. Abdulagatov & K. G. Ataev.
  1977. Control of the grape moth. Zashchita Rastenii 7: 24-5. [in Russian].   Manjunath, T. M. 1985. India - Maconellicoccus hirsutus
  on grapevine. FAO Plant Prot. Bull. 33: 74.   Marcelin, H. 1985. La lutte contre les
  tordeuses de la grape. Phytoma
  370: 29-32.   McKenzie, L. M. & B. P. Beirne. 1972. A grape leafhopper, Erythroneura
  ziczac (Homoptera:
  Cicadellidae), and its mymarid (Hymenoptera) egg-parasite in the Okanagan
  Valley, British Columbia. Canad. Ent. 104: 1229-33.   Niyazov, O. D. 1969. The parasites and predators of grape
  mealybug. Zashchita Rastenii 14: 38-40. [in Russian].   Pickett, C. H., L. T. Wilson, D. Gonzalez & D. L.
  Flaherty. 1987. Biological control of variegated grape leafhopper. Calif.
  Agric. 41: 14-16.   Rizk, G. A., I. B. Sheta & M. A. Ali. 1978. Chemical
  control of mites infesting grape-vine in middle Egypt. Bull. Ent. Soc. Egypt, Econ. Ser. 11: 105-11.   Rzaeva, L. M. 1985. Parasites and predators of the grape mealybug (Planococcus ficus Signoret) and
  introduction of new natural enemies into the eastern Transcaucasus.
  Biologicheskikh Nauk 4: 34-9.   Saunders, M. C. & J. N. All. 1985. Association of
  entomophilic rhabditoid nematode populations with natural control of first
  instar larvae of the grape root borer, Vitacea
  polistiformis, in concord
  grape vineyards. J.
  Invert. Path. 45: 147-51.   Schruft, G. 1972. Les tydéidés (Acari) sur vigne. OEPP/EPPO Bull. 3: 51-5.   Schruft, G. A. 1986. Grape. p. 359-66. In:
  W. Helle & M. W. Sabelis (eds.), Spider Mites Their Biology, Natural
  Enemies and Control. Vol.
  1B. Elsevier, Amsterdam. 458 p.   Schwartz, A. 1987. Seasonal occurrence of a predaceous mite Amblyseius addoensis
  Van der Merwe & Ryke (Acari: Phytoseiidae) on table grapes. S. Africa J. Enol. Vitic. 8: 78-9.   Settle, W. H., L. T. Wilson, D. L. Flaherty & G. M.
  English-Loeb. 1986. The variegated leafhopper, an increasing pest of grapes.
  Calif. Agric. 40: 30-2.   Tanigoshi, L. K., S. C. Hoyt & B. A. Croft. 1983. Basic
  biological and management components for mite pests and their natural
  enemies. p. 153-202. In: B.
  A. Croft & S. A. Hoyt (eds.), Integrated Management of Insect Pests of
  Pome and Stone Fruits. John Wiley-Interscience, New York. 454 p.   Trichilo, P. 1986. Influence of the host plant on the
  interaction of spider mites with their natural enemies in a cotton
  agroecosystem. Ph.D. dissertation, University of California, Davis.   Wheeler, A. G., Jr., & G. L. Jubb, Jr. 1979. Scymnus cervicalis Mulsant, a predator of grape phylloxera, with
  notes on S. brullei Mulsant as a predator
  of woolly aphids on elm (Coleoptera: Coccinellidae). The Coleopterist Bull.
  33: 199-204.   Williams, D. W. 1984. Ecology of a blackberry-leafhopper-parasite
  system and its relevance to California grape agroecosystems. Hilgardia 51:
  1-32.   Wilson, L. T., D. L. Flaherty, H. Andris, W. W. Barnett, D.
  Gonzalez & W. Settle. 1986. The variegated leafhopper: An increasing pest
  of grapes in the San Joaquin Valley. Proc. 1986 San Joaquin Valley Grape
  Symposium. p. 27-9.   Wilson, L. T., D. L. Flaherty, W. Settle, C. Pickett & D.
  Gonzalez. 1987. Managing the variegated leafhopper and grape leafhopper.
  Proc. Table Grape Symposium 1987: 5-11.   Wilson, L. T., M. A. Hoy, F. G. Zalom & J. M. Smilanick.
  1984. Sampling mites in almonds: I. Within-tree distribution and clumping
  pattern of mites with comments on predator-prey interactions. Hilgardia 51:
  1-13.   Winkler, A. J., J. A. Cook, W. M. Kliewer & L. A. Lider.
  1974. General Viticulture. Univ. Calif. Press. 710 p.   Yasnosh, V. A. & V. I. Mjavanadze. 1983. On the efficiency
  and rational use of Cryptolaemus
  montrouzieri against plant
  pests in the Georgia SSR. In:
  Proc. 10th Intern. Cong. Plant Protection 2: 798 p.   Zheng, Y., K. Daane, W. Barnett, K. Hagen, H. Andris & W.
  Peacock. 1990. Evaluation of release with Chrysoperla
  carnea for control of
  variegated leafhopper. USDA-ES Smith Lever Integrated Pest Management Proj. Develop.,
  Interim. Rept. 1990.     |