Annual Reviews www.annualreviews.org/aronline

Annu. Rev. Entomol.1992. 37:479-503 Copyright© 1992 by AnnualReviews Inc. All rights reserved

ROLE OF ANTS IN PEST MANAGEMENT

M. J. Way Imperial College, SilwoodPark, Ascot, Berks. SL5 7PYUnited Kingdom

K. C. Khoo Universiti Pertanian ,43400 Serdang, Selangor, Malaysia

KEYWORDS: beneficial species, biological control, , competition, habitat diversity

INTRODUCTION Ants, with an estimated world population of 1015 adults (188), are most abundant in the tropics wherein rain forests they mayrepresent betweenone third and half of the biomass (32). About two hundred species of ants have been recorded in one locality in Papua NewGuinea (187), and they also retain rich diversity in sometropical crops (76, 134). In general, ants are less common,with fewer species, outside the tropics (120, 187), but they maystill be ecologically important, as in a European grassland where about 140 workers per m2 consumedapproximately 200 times their biomass annually (71). Theyare usually least commonand diverse in disturbed arable habitats (120). In view of their abundance,their stability as populations, and their feeding habits, ants have a major influence in manyhabitats (17, 30, 45, 59, 63, 118, 127, 188). As predators of pests, they maybe useful in pest management,but such positive attributes must be weighed against possible disadvantages. Besides acting as biological-control agents, some ants are important in pollination, soil improvement,and nutrient cycling (45). In contrast, some feed on or disturb plants and mayact as vectors of plant diseases, benefit 479 0066-4170/92/0101-0479502.00 Annual Reviews www.annualreviews.org/aronline

480 WAY & KHOO

damagingHomoptera, and attack or irritate humans, domestic , and other beneficial organisms(162, 168). Virtually all species that prey on pests also possess somepotential disadvantages. This review briefly summarizesrelevant aspects of ants’ feeding habits and general ecology, followedby discussion of beneficial species and their attrib- utes, and of howecological conditions favoring their use can be manipulated for improved pest management.

FEEDING HABITS Significance of Honeydew-Producing Homoptera Predatory ants that are recognized as important in pest managementare mostly omnivorousand rely also on plant foods. For example, a Formicarufa diet comprised 62%honeydew; 5% resin, fungi, carrion, and seeds; and 33% insect prey (179). In particular, ant-attended honeydew-producingHomoptera provide a dependable energy food supply needed for large stable populations of certain ants to maintain consistent protection of the plants on whichthey forage. The relationship confers mutual benefits to ants and Homoptera(175). Recent work (72) highlights the fact that particular Homopteraare essential for biological-control success. In contrast, predatory ant species that do not utilize Homoptera,such as the highly voracious army and driver ants, are raiders that only temporarily suppress most prey populations in a particular locality. Ant-Prey Interrelationships

CHOICE OFPREY Predacious ants can be classified simply as specialists or generalists (187). Mostso-called scavenger ant species prey on small organ- isms, including insect eggs. The specialists do not seemto be significant in biological control, though somemust have an impact, for example,on certain pest termites. The generalist ant predators include those that are recognizedas important in biological control, and somedata are available on the range of prey species captured by these ant species (2, 7, 53, 95, llS, 128, 181). Larger ants tend to attack larger prey and maydisregard, or not see, the smaller prey attacked by smaller ants (137, 174, 176). This relationship is doubt related to the bioenergetics of costs and returns in prey capture and transport by different-sized ants. A hierarchy of ant influence on major insect groups has been suggested (76) but is not borne out by the evidence. For example, a single group such as the varies widely from resistant to susceptible to predation, and other evidence refutes the hierarchy hypoth- esis (128). Ants can repel other organisms, perhaps through chemical repellents (139, 167). Hostility does not always appear to be a key attribute because Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 481

Anoplolepis longipes can exclude somevertebrates and other large animals from its territory (52), unlike the muchmore aggressive Oecophyllaspecies. Yet A. longipes does not attack manysmaller organisms, including insect pests, that Oecophyllaspp. kill (172). Dolichoderusthoracicus incidentally disturbs pests on which it does not prey (36, 72, 161).

PREYDEFENSE Many possess generalized defense mechanisms such as flight, jumpingaway, or droppingoff the plant whenthreatened, but these maynot be effective against ants that forage at different levels of the ecosy- stem (53). Size and other physical attributes aid in prey defense. For example, Formica and Camponotus spp. captured 56% of first-instar gypsy larvae, but this amountdecreased to 4.8%as larvae grew (184). Larger larvae were attacked, but manyescaped. Formica polyctena preys on larvae and adults of the Colorado potato Leptinotarsa decemlineata, but the smaller Myrmicalaevinodis does not. It is repelled by the beetle’s chemical defenses, which the Formicaspecies disregard (40). This observation raises the question of evolution of specific prey defense mechanismsagainst ants. Life in galls, mines, webbedleaves, or masses of spittle mayhave evolved partly as protection from ant predation (53), though leaf miners are heavily preyed on by some ants (25, 137). Potential prey maysequester ant-toxic compoundsfrom larval host plants (12, 64), and the repugnatorial glands some hemipteran predators protect them from Solenopsis invicta (125). Evolved protective mechanismsmay include out-of-phase survival in ant-free space (53), whichquestions the suggestion (138) that insect herbivores difficulty in countering ant predators. Although long stable evolutionary association in some natural habitats may favor development of some pro- tective mechanismsagainst ants (53), this situation contrasts strikingly with that of most agricultural systems. Workcomparable in detail to that of Heads & Lawton(53) still needs to be done in artificial habitats as a basis for improveduse of predatory ants.

COMMUNITY AND POPULATION DYNAMICS

Majer (92) classified ants into status categories of dominant; subdominant, which can attain dominant status in the absence of dominant ants; and nondominant,which live within or betweenthe territories of dominantants. Dominantants include species that are most conspicuouslyuseful for biologi- cal control. A dominantant is numerically the most abundant ant species in its area of occupation from which it characteristically excludes all other dominantant species, though this exclusion is not always clear cut (76, 132, 172, 177, 178). A single species may dominate a very large area; for example, A. Annual Reviews www.annualreviews.org/aronline

482 WAY & KHOO

longipes had up to 300 queens/nest, a nest density of 700/ha, and a population sometimesexceeding 10 million/ha over 1250 ha in the Seychelles (51), and super-colonies of Formica yessensis in Japan comprised some 306 million workersand morethan one million queens in 45,000 nests in a territory of 2.7 kmz (55). Colonies of most dominant species occupy smaller areas, each forming part of a mosaic of interdigitating colonies of the same or other dominantspecies (84, 92, 94). In relatively stable habitats, such as in the soil of temperate grasslands, coexistence can be very stable (121, 122). Con- ditions are naturally less stable in the aerial environment, especially when simplified by agriculture in whichuseful indigenous ants such as Oecophylla and Dolichoderus spp. maybecome prey to invading, often exotic, species of Solenopsis, Anoplolepis, and Pheidole--"extirpators," to use Wilson’s (188) terminology. In somecircumstances, species can ebb and flow (48), though there is usually a notable hierarchy (13, 188). The manipulation of crop conditions to alter the rank order in favor of beneficial species and against harmful species is fundamental to the use of ants in pest managementand is emphasizedlater in this review.

PREDATORY ANTS AS BIOLOGICAL-CONTROL AGENTS

Literature on beneficial and potentially beneficial predatory ants is available for the Old World(76) and for cocoa in the NewWorld tropics (22). Gotwald (45) gives a few worldwide examples. Farmers were first to recognize the beneficial role of five species (16, 23, 60, 108, 113,131). Published workhas highlighted seven genera of dominant ant species--Oecophylla, Dolicho- derus, Anoplolepis, Wasmannia,and Azteca in the tropics, Solenopsis in the tropics and subtropics, and Formicain temperate environments. This section includes case studies of the seven important genera and also discussion of the role of more inconspicuous ant species, especially as egg predators.

Oecophylla Species Twohumid-tropics species, O. longinoda in Africa and O. smaragdina in Asia and Australia, have biologies so similar that they can be treated as one. They are active throughout the year, and their distribution and abundance depends on evergreen trees and shrubs (15, 56, 173) with suitable leaves for silk-woven leaf nest construction. Individual colonies, which are mutually antagonistic, maycover up to 1600 mz and comprise approximately a million workers and brood (56, 57, 173). They are demarcated by no-ant boundaries where posturing, but rarely fighting, occurs (56, 57, 76, 173) Colonies are monogynous(164, 173), and the queen is not replaceable Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 483

(164, 166). Monogynyis no doubt responsible for the outstanding colony organization of Oecophylla spp., which is based on pheromonesproviding "the most complexof such repertoires thus far discovered in ants" (58). Perhaps pheromonescould be used to improve biological control by enhanc- ing competitiveness against other ant species.

ROLEIN PESTMANAGEMENT A Chinese publication reputedly written in 304 ADstates that "in the market the natives of Jiao-Zhi sell ants stored in bags of rush mats. The bags are all attached to twigs and leaves, which, with the ants inside the nests, are for sale. In the south, if the Gantrees (mandarin orange) do not have this kind of ant the fruits will all be damagedby many harmful insects and not a single fruit will be perfect" (60, 108). This, the earliest knownexample of biological control, is still practiced after 1700 years (190). Oecophylla spp. workers attack manyinterfering animals, including hu- mans, and kill a wide range of for food (173). They do not appear to perceive sessile animals such as the non-honeydew-producingDiaspididae, though they must recognize honeydew-producingHomoptera with which they are mutualistically associated (174, 175). This is also evident from their ¯ -destruction of-such Homopterathat exceed the honeydewrequirements of the colony (174). O. longinoda workers do not attack very small insects such as parasites of their attended Homoptera,though someparasites are severely hampered(174). Predacious larvae of someLepidoptera (173) and Coccinelli- dae (164) seem adapted to succeed within O. longinoda colonies. No doubt the highly organized aggressive predatory behavior, combined with extensive foraging throughout the area occupied by a colony, explains the success of Oecophylla species in killing or driving awaymany pests or potential pests, notably and foliar-feeding Coleoptera. Table 1 lists localities where work on such predation has been done. Our recent observations that the ant can help protect cocoa against rodents and oil palm against some lepidopterous defoliators indicates that the potential of Oecophyllaspp. has not been realized. The effect of Oecophyllaspp. against the , Arnblypelta cocophaga in the SolomonIslands, and Pseudotheraptus wayi and Pseudotheraptus devastans in Africa exemplifies the use of these ants in pest management.The pests cause identical damageto by feeding on female flowers and young nuts. Estimates of nut loss range from about 30--65% according to region (164; M. J. Way, unpublished data), to which should be added up 50%yield loss from severely damagednuts that survive to maturity (69). Locally, losses maybe catastrophic, as indicated by a 10-fold yield increase after an experimental chemical treatment (171). palms occupied by thriving colonies of Oecophylla species are Annual Reviews www.annualreviews.org/aronline

484 WAY & KHOO

Table 1 Reports of Oecophylla spp. as beneficial predators

Ant species Pest Region References Coconuts O. longinoda Pseudotheraptus wayi East Africa 164, 171 Pseudotheraptus devastans 69 O. smaragdina Amblypelta cocophaga Solomon Islands 14, 119 Axiagastus cambelli Solomon Islands 79 NewBritain 6 112 Brontispa longissima Solomon Islands 144 Promecotheca spp. Papua New Guinea 107 Oil palm O. smaragdina Crernastopsyche pendula and others Malaysia G.F.a Chung Cocoa O. longinoda Distantiella theobroma West Africa 76, 99 Crematogaster spp. West Africa 149, 150 O. srnaragdina Helopeltis theobromae Malaysia 177 Arablypelta theobromae Papua New Guinea 153 Pseudodoniella laensis Papua New Guinea 153 Pantorhytes spp. Papua New Guinea 135, 153 Pantorhytes biplagiatus SolomonIslands 143 Rodents Malaysia M.J.b Way Coffee O. longinoda Antestiopsis intricata 76 Citrus O. smaragdina Tessaratoma papillosa and other China 60, 108 Heteroptera Rhynchocoris humeralis China 190 Rhynchocoris serratus 34 Eucalyptus O. smaragdina A. cocophaga Solomon Islands 91 Mango O. smaragdina Cryptorrhynchus gravis 170 Timber trees O. longinoda Scolytidae Platypodidae Ghana 76

Personal communication. Personalobservation.

completely, or almost completely, protected from damage by the pests, as is evident when O. longinoda is deliberately killed and when crops on occupied palms are compared with those on adjoining unoccupied ones (66, 172). Decreased damage and increased yields are associated with increasing O. smaragdina populations (143). Unfortunately, relatively few coconut plantations in Africa and the Solo- mon Islands are well colonized by Oecophylla spp. because other useless dominant competing ant species have displaced them (119, 172). This Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 485

observation stimulated work on causes of displacement and on howto en- hance abundance of Oecophylla spp. (15, 48, 49, 143, 172). Investigators recognized that diversity in the form of appropriate shrub and ground vegeta- tion benefits O. Ionginoda(173) and O. smaragdina(48). Interplanting with favored trees therefore benefits Oecophylla spp. both inherently and also indirectly by strengthening their ability to competewith other ant species (26, 143, 173). Promisingresults have been obtained with insecticides to control competingants and so permit natural increase of Oecophyllaspp. populations (26, 143, 163). The bait Amdro(hydramethylnon) has been particularly successful in selectively controlling Pheidole megacephalain East Africa (83) where it is the major competitor of O. longinoda (172). Insecticides provide valuable componentsof well-established integrated pest management(IPM) in the Ivory Coast (26, 66-69) where they are used control P. devastans and competingants as a supplementto biological control by O. longinoda. Insecticide use on O. longinoda-unoccupiedpalms is based on treatment thresholds for the pest except where >60-70%of the palms are colonized by O. longinoda--a level at which damagebecomes insignificant (66, 172). In the Ivory Coast, IPM practices also include artificial in- troductions of O. longinoda and encouragementof appropriate vegetation (26). In conclusion, L~lthoughintensive treatment with insecticides can directly control P. wayi, this causes outbreaks of Diaspididae, no doubt through destruction of their natural enemies(171). Moreoversuch treatments can only be justified for protecting accessible dwarf palms used for high-value seed. An average of one P. wayi or A. cocophagaper palm can cause very serious damage,putting a premiumon intensive application of insecticides as well as precluding the use of conventional density-related natural enemies. Like any IPM system, the use of Oecophylla spp. requires organization (26). The aggressiveness of Oecophyllaspp. is a constraint, a characteristic that has made O. smaragdina unacceptable to cocoa-plantation staff in Malaysia, despite its excellent control of the seriously damagingmirid Helopeltis theo- bromae (177). Dolichoderus thoracicus In parts of the humid Southeast Asian tropics, this ant nests in suitable crevices; very large populations can be found in the spadices of coconut palms (178), betweenappressed or folding leaves (72), and in insolated leaf litter the ground(72, 178). Wherenesting sites are small and unstable as in cocoa, the ant is benefited by artificial nests in the trees (72, 161). Suitable nesting sites are essential for the large populationsof the ant neededto exert biologi- cal control (72, 178). D. thoracicus is polygynous, and a dense colony may cover an area of manyhectares (178); sometimescolonies are relatively small Annual Reviews www.annualreviews.org/aronline

486 WAY & KHOO

and separate as in a mixed cocoa-coconut plantation, where each radiates from a particular coconut palm. Here, inter-colony aggression occurs, but colonies seemingly anastomose as the ants becomemore abundant (178).

ROLEIN PEST MANAGEMENTIn the early 1900s, cocoa planters in In- donesia observed that less mirid damagewas associated with the presence of D. thoracicus on cocoa, so they introduced ants into new areas. Subsequent research improvedthese introductions (36, 131, 161), but interest declined during an era of insecticide overdependence,until the 1980s (5) whenwork also began in Malaysia (72, 177, 178). D. thoracicus is not aggressive, and so it is not a nuisance to plantation staff. It deters other insects from places whereit concentrates densely, as whenattending Homopteraon cocoa prds (72, 161). In Malaysia, it associ- ates with the mealybugCataenococcus hispidus, which does not appear to decrease yield (72). D. thoracicus is particularly successful in protecting cocoa against the mkidsHelopeltis antonii and Helopeltis theivora in Indonesia and H. theob- romae in Malaysia, the feeding lesions of which kill and damagepods and young shoots. However,D. thoracicus is locally distributed and, even when present, maybe insufficiently abundant to protect cocoa. Constraints include competition with other ants and insufficient nesting sites and honeydew- producing Homoptera,particularly in the wet season (5, 10, 37, 72, 161)._ Recent establishments of D. thoracicus on cocoa (5, 72) have been made follows: (a) ground treatment of the introduction area with an insecticide spray (Indonesia) or bait (Malaysia) to suppress antagonistic ants; (b) ment of bundles of coconut leaflets or polythene bags containing cocoa leaf litter as artificial nests in already heavily colonized areas and, whenwell colonized, removal to cocoa trees in the introduction area; (c) artificial colonization with mealybugsin the introduction area; (d) fresh introductions of D. thoracicus (Indonesia) or mealybugs(Malaysia) if needed; (e) leaving the proximal ends of harvested pods on the tree to conserve mealybugs (Indonesia); (f) maintenanceof cocoa and coconut palm leaf litter to provide ground-nestingsites for the ants. In conclusion, D. thoracicus is a valuable biological-control agent in its own right and also as part of an IPM program involving spot spraying of inadequately protected trees (5,177). Useof other beneficial ants, notably smaragdina, could be integrated with that of D. thoracicus (178). Formica rufa Group Gosswald (43, 44) and others (2, 21, 47, 180, 183) have comprehensively covered the extensive literature on this complexof eight species. In their temperate forest environment,Formica spp. are inactive during winter; activ- Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 487

ity at other times depends on temperature. Subspecies may be either monogynousor polygynous (2), and colony boundaries are sometimes unclear and mayonly be apparent during reestablishment in spring (89). Colonies maybe very large; for example, a single F. lugubris colony covered over 90 ha (19).

ROLEIN PESTMANAGEMENT The value of Formica spp. against defoliat- ing outbreak pests in temperate forests has been recognized in Germanysince the 19th century (41, 43, 44). Unlike the low-density endemicpests that can be controlled by Oecophylla spp. and D. thoracicus, the recognized pests controlled by Formicaspp. are high-density epidemic species whoseperiodic rapid rise to abundanceputs a premiumon density-dependent predation. The ants’ predatory potential is exemplified by an estimated eight million insects killed in a year by a medium-sized nest of F. polyctena (179) and some 14,000 tons of insects by the approximatelyone million ant nests of the F. rufa group in the Italian Alps (116). Consequently, damagearound Formica spp. colonies maybe minimalduring outbreaks of defoliating caterpillars, the protection being inversely related to distance from the nest (2, 8, 9, 180, 182). In particular, "green islands" surround colonies of F. polyctena during outbreaks of the lepidopteran Panolis flammea;the ants disturb ovipositing adults, kill larvae on the trees and on the ground, and kill pupae beneath the soil (8, 9, 181). In fact, Formicaspp. kill manydifferent defoliating pests in Europeanforests (2, 44, 114), from whichtree growthmay benefit (e.g. 186). F. polyctenaand F. lugubris are particularly useful for artificial establishment in different climatic zones (21, 41, 116, ll7). They are favored because they reach high population densities, are facultative predators active over a long season day and night at all levels of the forest, and are capable of killing both active and quiescent stages of different prey species, notably the caterpillar pests on which they concentrate during outbreaks. Whenprey is scarce, they maintain their large populations on the honeydewfrom attended Homoptera (175). The large many-nest,polygynous ant colonies have been established artifi- cially in manyEuropean plantations (30, 41, 42, 44, 47, 74, 117, 142, 157, 182), and F. lugubris has been successfully transferred to eastern Canada(31, 103). Recommendationsfor pest managementinclude cultural practices that assist the ants (e.g. 44, 152, 189) and use in combination with microbial pesticides (117). The relative ease with which suitable Formicaspp. can be established in temperate environments is probably associated with com- parative lack of competition from other dominantant species, in contrast to most tropical situations. Although Formicaspp. kill very large numbersof pest insects during a pest outbreak, about 7%of prey may be beneficial species (8, 41), rising to approximately 15-20%in nonoutbreak situations Annual Reviews www.annualreviews.org/aronline

488 WAY & KHOO

(2). The ants partly deterred Coccinellidae, yet whenabundant, the latter could still eliminate populations of F. polyctena-attended aphids (179). Gridina (50) showedthat a diverse but smaller communityof other predators survived where F. polyctena was abundant. The role of these other beneficial species has not been determined. Though some prey importantly on the Homopterathat the ants attend (175), the ant protection enables someHomop- tera, as on beech trees (Fagus), to reach damagingabundance (106). In conclusion, although the use of the Formicarufa group maysometimes be undesirable, muchevidence supports their role in usefully protecting trees from somedamaging defoliating pests. Moreover,their stabilizing influence on pests and potential pests in forest ecosystems must be important and justifies further study. Azteca Species The value of these fiercely predacious tree-nesting NewWorld tropical ants was recognized by the KayapoIndians who used them against leaf-cutting ants in Brazil (22, 113). In Trinidad, Azteca sp.-occupied citrus trees are damagedmuch less by the leaf-cutting ant Atta cephalotes than unoccupied ones, and experimentaldestruction of Azteca sp. colonies led to A. cephalotes defoliation of 80%of the trees within two weeks(70). Manypest, or potential pest, species are excluded from the colony area of Azteca spp. (22, 62) through aggression and repellency (11, 139, 167). Although Azteca sp.- colonized cocoa had higher yields than adjoining uncolonized trees, and some growerscontinue to encourageAzteca chartifex by distributing nest fragments amongtheir plantations, this traditional practice (156) is criticized becausethe discomfort the ants cause to people and damageby their attended Homoptera are said to outweigh the benefits the use of the ants confers (22). More thoroughinvestigation of the role and use ofAzteca spp. is needed(62, 77).

Wasmannia auropunctata This ant is sometimesregarded as a pest in its native tropical America(160), and, as an introduced species, can greatly affect the indigenous insect com- munity (20, 88). Its polygynousand apparently small but abundant colonies are associated with humidconditions in perennial, mostly tropical, environ- ments (88). Twoaccidental introductions exemplifyits role as a valuable, potentially valuable, biological-control agent. In the Cameroons,local farm- ers establish nests in cocoa plantations, having recognized this ant’s value against cocoa mirids (16). Appearing recently in the SolomonIslands, controls a serious pest of coconuts, Amblypelta cocophaga, and is also displacing two other dominant pest ants, Iridomyrmexcordatus and , which do not protect coconut palms from A. cocophaga (90). Even though W. auropunctata has a painful sting whenseverely disturbed, it Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 489

is remarkable that this very small, slow-movingant can displace fiercely competitive species. Perhaps it uses a chemical repellent. In view of its potential importance for biological control in its indigenous (G. Pollard, personal communication)as well as someexotic environments, the ecology and impact of W. auropunctata should be studied in muchgreater detail. Anoplolepis Species Anoplolepis longipes probably originated in Africa but nowoccurs worldwide in the tropics where it forms super-colonies (51). It is a nuisance pest homesand can kill or disturb domestic animals and harm plants directly and indirectly (52), but it is not conspicuouslyaggressive towardspeople and does not bite or sting. It has destroyed and displaced the beneficial O. longinoda from somehabitats in East Africa (172) and is similarly recognized as a major constraint to establishment of D. thoracicus for control of cocoa capsids (72, 161), although A. longipes itself can provide someprotection to cocoa (80). A. longipes usefully protects coconut palms from Amblypelta cocophagain the SolomonIslands, in contrast to its ineffectiveness against the closely related and identically damagingP. wayi in East Africa (14, 48). Perhaps the SolomonIslands, it depends more on prey for food (49). In Papua New Guinea, it is encouraged for control of Pantorhytes spp. (Coleoptera) cocoa and becauseit displaces other ant species that can transmit Phytopthora spp. (102, 133, 140). It is also a valuable predator of Pseudodoniellalaensis on cocoa (153) and is recommendedin IPM programs (140). In the chelles, although condemnedas a nuisance pest, it seems able to protect coconuts from the severely destructive Mellitomma insulate and Oryctes monoceros(81). The latter is presumablydisturbed rather than killed, but this assumption should be investigated in view of the worldwide tropical im- portance of rhinoceros . is largely limited to well-drained, usually sandy habitats with good insolation (172) and is considered a pest in because its attended Homopteraseriously damagecrops such as citrus (148). In Tanzania, however, very dense populations can protect coconut palms from P. wayi (82) though populations with normal abundance do not (172). Whenthe ant is very abundant, damageby its attended Homopteramight be unacceptable. In conclusion, A. longipes has important biological-control attributes that can usefully be encouragedin places whereit is clearly beneficial, although it sometimesneeds to be controlled as a pest elsewhere. Solenopsis Species This includes three NewWorld species of fire ant, S. getninata in the hotter climates, and S. invicta and S. richteri from subtropical South Amer- Annual Reviews www.annualreviews.org/aronline

490 WAY & KHOO

ica, whichhave been introduced to the southern United States. The introduced species are opportunists that exploit and thrive in disturbed agricultural habitats (158, 169). At least 6000 rapidly growingcolonies/ha, each some- times comprising groups of queens, maybe established on newly available land (99, 159), but ultimately only about 50-60 colonies mature (105). Normally only one queen survives in each mature colony of about 40,000 workers; and then the colony becomesterritorial (159). Differences in colony organization pose economically important unansweredquestions (158). In the USA,the two introduced species are nuisance and public-health pests but are not regarded as major pests of crops (4, 84-86). Control measures have cost some$200 million since 1957 (4, 84, 162). S. invicta is, however,a valuable predator (123), especially against somepests of sugar cane (1, 123), cotton (27, 28, 65,100, 101,145,151), and other crops (75,123,185) and somepests of veterinary importance (123). S. invicta maynot harm other predacious insects in cotton fields (125, 147), and sometimes chemical control of the ant has madepests worse (1, 54, 87, 124). Current emphasis therefore on preservation and enhancement,especially through cultural prac- tices and selective use of chemicals in situations where the benefits of S. invicta outweighits disadvantages (3, 65, 123, 146). Reagan(123) discusses opportunities for sugar cane pest managementbased on understanding in- terrelationships between the crop, its weeds, ant predators, and other in- vertebrates. The indigenous S. geminata may also be a valuable predator, sometimes of weed seeds (18, 24, 61, 127, 136). That it can decrease Sitophilus sp. numbersby 98%on corn is striking evidence of its potential (127). In conclusion, Solenopsis spp., particularly the introduced S. invicta, have undoubtedbiological-control attributes such that the ants need to be encour- aged in localities where they do little or no harm. Ants as Egg Predators Goodevidence shows that ants prey on eggs of pest species in manydifferent countries and habitats (Table 2). For example,in Sri Lankavirtually 100% eggs of Opisina arenosella were removed within 24 h by Monomorium floricola (176). Solenopsis invicta was part of a complexkilling over 70%of eggs of Heliothis virescens in 24 h on cotton whereratios of predators to prey ranging from 2:1 to 200:1 seem able to prevent significant pest damage(100, 101). On sugar cane, over 90%of eggs and small larvae of Castnia licus (24) and 92%of eggs of Eldanasaccharina (38) were killed by ants. Pheidole spp. are major predators in complexesthat can kill over 95%of eggs of Alabama argillacea (46) and some 80%of Diabrotica spp. eggs in the soil (126). Certain cultural practices benefit predation, for example maintaining bare strips betweenrows of citrus (61) and someforms of intercropping (l 11). Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT491 Annual Reviews www.annualreviews.org/aronline

492 WAY & KHOO

significance of ant predation on eggs is evident from the conclusion that Cactoblastis cactoruminadequately controlled prickly pear in South Africa partly because ants killed up to 70%of its eggs, although this effect was harmful (129). In conclusion, ants alone or as an important part of a predator complex(61, 101, 185) can cause very large mortalities of eggs and so can contribute importantly to natural control. Morespecific case studies are neededto assess the importance of such mortality, especially because increased egg mortality can sometimesbe compensatedfor by decreased larval mortality (165; M. J. Way, unpublished data).

Role of Nondominant Ant Predators

Inadequateattention has been given to the manyant species that are relatively inconspicuous predators and/or scavengers of eggs (Table 2) and other life stages of pests. Manyare categorized as sub- or ~nondominants(92) and are often relatively small, "passive aggressors" (78), someof which, as "in- sinuators" (188), can flourish even where other ants dominate. For example, these ants include species ofMonomorium,Technomyrmex, and Tetramorium in the presence of Oecophylla smaragdina(176). Someare important preda- tors of pests that the larger aggressive dominantants do not attack (25, 130, 137, 154, 176, 181). Further understanding of their roles in pest dynamics and in pest managementremains a challenge for the future.

PROMOTING USE OF ANTS IN PEST MANAGEMENT Favorable Ant Qualities Importantattributes of useful ant species (,30, 96, 97,127) are listed by Risch & Carroll (127) as follows: (a) they are very responsive to prey density; they can remain abundant even when prey is scarce because they can cannibalize their brood and, most importantly, use honeydew-producing Homopteraas a stable source of energy; (c) they can store tbod and hence continue to capture prey even if it is not immediately needed; (d) besides killing pests, they can deter manyothers including some too large to be successfully captured; (e) they can be managedto enhance their abundance, distribution, and contacts with prey. Other useful criteria for ants as biological-control agents include broad habitat range and choice of species that are unlikely to be out-competedby other ants (96). Finnegan(30) lists desirable characteristics of certain Formi- ca spp., someof whichare relevant to other ants, including ability to hunt at different levels and to concentrate increasingly on a particular prey species as its population increases. Polygynyis a useful attribute because colony frag- ments can easily be transferred to establish newcolonies. Manyant species Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 493

have insufficient desirable qualities so that they, like indigenous ants of Canadianforests, are not good for biological control (29). Undoubtedlythe most important attribute of useful or potentially useful predatory ants is stability as large populations, whichtogether with efficient recruitment enables the ants to react quickly to surging numbersof a pest. Ants such as Formicapolyctena can therefore cause direct density-dependent mortality, unlike the characteristically delayed action of nonsocial natural enemies. Another consequenceof stability of large predatory ant populations is their unique ability, through efficient foraging, to protect plants from low-density pests. For example, O. longinoda protects all year against the coreid P. wayi, which can cause catastrophic damageto coconut palms at densities of one to two individuals per coconut palm, a level at which conventional natural enemies are ineffective. Attended honeydew-producing Homoptera,besides ensuring local stability of large ant populations, can encourage foraging for prey on plants or in fields where they occur (104, 109), and in forests (30) where a ground-nesting ant mayotherwise confine foraging to the forest floor (184). Well-knownmutualisms involve plants with specializations attractive to ants that in return protect the plants from herbivores(7, 63). Suchattributes, however, are characteristic of plant species of little or no economicim- portance. Perhaps excluding extra-floral nectaries, coevolution does not seem to have led to such specializations in plants of notable economicimportance. Manipulations That Favor Ants in Pest Management The proposal to protect, enhance, or introduce an ant for biological control can be rationalized by a sequenceof decisions, just as for any control practice (133). Onceit has been decided to makeuse of a particular ant, one must answer two main questions: first, howto suppress undesirable competingants that otherwisedisplace the desired ant or keep it too scarce to be effective, and second, howto improve other favorable conditions. These requirements are interrelated; for example, other favorable conditions will naturally favor competitive ability. Suppression of competingants is not always needed, for example in the use of Formica spp., which may have no significant com- petitors in their temperateforest environment,and of ants such as S. invicta that are invaders of open habitats. Colonies of undesirable species can be killed or suppressed locally ~y insecticides but will usually becomereestablished unless other conditions are created that inhibit reinvasion. Therefore, fundamental to use of an ant species in IPMis appropriate understandingof relevant aspects of its ecology and that of undesirable competingspecies.

SIGNIFICANCEOF THECROPPING SYSTEM Illuminating evidence supports the importance of certain crop mixtures for encouraging beneficial ants. Annual Reviews www.annualreviews.org/aronline

494 WAY & KHOO

Interplanted trees such as citrus and cloves strengthen the role of O. longinoda in control of coconut pests (173). This was also demonstrated with smaragdina against Amblypelta cocophaga in the SolomonIslands (143). Similarly, coconut palms with underplanted cocoa are muchless affected by Axiogastus cambelli (112) than are monocroppalms. Conversely, the palms benefit cocoa. Certain pests are worse under Leucaena shade than under coconuts including Pantorhytes szentivanyi, which is strongly associated negatively with coconuts and positively with Leucaenashade (135). Perhaps coconutsprovide essential food and nesting sites for beneficial ants, as they do for D. thoracicus protecting cocoa from H. theobromae(178). Shading different levels of vegetation maybe important. For example, the beneficial ant Macromischoidesaculeatus seems inherently to require a thick understory of a crop such as cocoa, whereas Oecophylla spp., if free from competition with other ants, can also flourish wherethere is relatively little shade (94). Appropriate coconut-cocoa planting regimes have been recommendedfor cocoa pest control (93). Ground vegetation suppresses some deleterious competing ants; for ex- anaple, Anoplolepis custodiens in East Africa depends on well-insolated soil for nesting and does not supplant O. longinoda in habitats where there is sufficient ground and shrub vegetation (172). There has been some con- troversy over the role of vegetation in relation to the control of A. cocophaga in the SolomonIslands (15, 48), but the conclusion must be that vegetation powerfully affects the outcomeof competition between dominant ant species and that success in manipulating vegetation to favor beneficial species de- pends on understanding the quality of its diversity. Several studies help towards such understanding (18, 48, 49, 76, 96, 97, 127). Ecological and applied ecological concepts (e.g. 98, 141) explain how exploiting species can dominate the unstable, less mature early stages of ecological succession and their arable crop equivalent, whereas differently adapted species require the stable environmentof more mature climax peren- nial systems. As plantation systems mature, dominant ant ~pecies change correspondingly (92). Manyinvasive exploiting species, such as someSole- nopsis spp., A. longipes, and Iridomyrmexhumilis, are adapted to the more open, less mature stages of natural succession and to the arable crop equiv- alents of these stages (e.g. 158). S. geminata, for example, quickly invaded the openhabitat of a cleared forest, but within a year decreaseddrastically as herb and tree vegetation becamereestablished (18, 127). This species favored by continuous mixed cropping cycles (136). In contrast, mature- ecosystem species such as D. thoracicus and Oecophylla spp. are no doubt denizens of natural forests (178). Habitats neither immature nor mature enoughto favor one or another kind of ant seemhighly unstable. For instance, in some semi-open cocoa-coconut plantations in Malaysia, four dominant Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 495

species, O. smaragdina,D. thoracicus, Crematogastersp., and A. longipes, coexisted (177). All were relatively uncommonand all competedin cocoa tree canopies where up to three species were foraging sparsely on a tree with no obvious territorial distinctions except around each species’ nests. Crops are grown in a wide range of ecological conditions from very immature arable systems through more complex mixtures of arable crops, combinations of tree and arable crops, and trees in monoculturesor complex combinations. The last most nearly approaches conditions in mature forests. At all levels, therefore, one should be able to manipulateconditions to favor a particular kind of ant, as is evident from recommendationsto maintain strips of bare soil to favor the open habitat species S. geminata(75), or to keep vegetational diversification and shading to favor moreclosed-habitat species (26, 97, 172). The approach therefore is to simulate in agricultural systems the key elements of the equivalent natural ecosystemthat benefit the chosen ant species. Carroll & Risch (18) studied and discussed aspects of this problemfor ants in an arable agroecosystem,and Greenslade (48) did similar work in a perennial agroecosystem. In the arable cropping system, muchmay dependon the ability of the ant to reinvade newlycultivated land quickly, as can S. geminata, especially if refuges are provided by strip-cultivated or mixed-cropsystems. In this respect, traditional slash and burn agriculture harms ants more than somecontinuous cropping systems (136). However,the "weed"species, S. invicta (158), seemsable to reinvade very quickly a large simple cotton monoculture(145). In the perennial system, the encouragement of ants such as Oecophyllaspp. dependsprimarily on creating conditions that are unfavorablefor open-habitat, invasive species becauseotherwise the latter almost invariably seem to dominate. So far, this section has contrasted the distinctive conditions favoring ants adapted to immaturehabitats with those adapted to more mature habitats. However,different species all adapted to the samehabitat also compete. In a mature habitat, the outcomeof competition betweenthe adapted species may dependon availability of their favored niches in the three-dimensionalmosaic (48, 76). Wherethe vegetation is relatively complex,as in a mixedplantation of tall trees, understorytrees, and groundvegetation, ant species are horizon- tally segregated (48, 49, 187). However,with vegetational simplification the lower-story vegetation, segregation changes to a morevertical arrange- ment such that species previously associated with lower stories begin to forage and even makesubsidiary nests in upper stories, as do Pheidole spp., which then compete with and displace Oecophylla spp. from coconut palm crowns (172). Finally, even where there is horizontal segregation of lower- and upper-story ant species, dominants adapted to a particular story still compete, as in coconut palm crowns in the SolomonIslands (15, 48, 49). Here, lridomyrmex cordatus has locally displaced O. smaragdina on palm Annual Reviews www.annualreviews.org/aronline

496 WAY & KHOO

crowns, and a recently introduced ant, W. auropunctata, has begun to dis- place both O. smaragdinaand I. cordatus (90). Reasons for the dominance hierarchy of such species are unknown.

CONCLUSIONS

The stability, social organization, and foraging behavior of somepredatory ants enable them to react quickly to increasing prey density, and also make them uniquely able to protect crops from loW-density pestL Such qualities. require dependence on honeydew-producing Homoptera that may sometimes be made harmful by ant attendance. Cost-benefit judgments are therefore needed when such ants are to be used. Predacious ants also affect other natural enemies, but less than might be expected, and mayindeed benefit some. Ants tend to overlap the food niches of other predators and mayforce them into one competitive system. Whether overall biological, control is benefited by such interactions is unknown.Work on the role of ants as part of overall natural-enemy complexesis needed. In addition, inadequate attention has been given to understanding ant-prey in- teractions. Research such as that done in somenatural habitats needs to be undertaken in agroecosystems. Behavioralattributes that enable one species, for example,a very small and apparently inoffensive species, to dominate over larger more aggressive species are not understood and need detailed investigation. Studies of this type should provide valuable clues to manipulating systems in favor of some beneficial species. Biological-control attributes of manyrelatively inconspicuous nondomi- nant ants have been inadequately studied. Somespecies maybe valuable in their ownright, but manyalso makea significant contribution to overall natural mortality, which needs to be understood muchbetter than it is at present. The results are promising from someecological approaches to manipulating beneficial ants by cultural practices and habitat modification. Moreemphasis is needed on practical application, especially since someants have sharply contrasting pest and beneficial attributes, e.g.S, invicta. Since eradication is impossible, the emphasisshould be on enhancingtheir role in habitats where they are beneficial, while controlling them elsewhere. Such approaches need not be incompatible. Althoughthe introduction of exotic predatory ants for biological control is potentially hazardous, it should not be discounted. In this context, workis needed on someaccidentally introduced species that have important biologi- cal-control attributes, e.g.W, auropunctata. Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 497

Finally, in some circumstances, ants are uniquely useful, as when they are the only alternative to intensive insecticide treatment, or where alternative practices are uneconomic or impracticable.

ACKNOWLEDGMENT We are most grateful to the British Council for funding that enabled us to work together on the review.

Literature Cited

1. Adams, C. T., Summers, T. E., Lof- parasitas do cacau ha Bahia. Salvador, gren, C. S., Focks, D. A., Prewitt, J. C. Brazil 1. C. B. Boletim Technico No. 5. 1981. Interrelationships of ants and the 112 pp. borer in Florida sugarcane 12. Bowers, M. D., Latin, Z. 1989. Ac- fields. Environ. Entomol. 10:415-18 quired chemical defense in the lycaenid 2. Adlung, K. G. 1966. A critical evalua- butterfly, Eumaeus atala. J. Chem. tion of the Europeanresearch on the use Ecol. 15:1133-46 of red wood ants (Formica rufa group) 13. Brian, M. V. 1952. The structure of a for the protection of forests against dense natural ant population. J. Anim. harmful insects. Z. Angew. Entornol. Ecol. 21:12-24 57:167-89 13a. Brian, M. V., ed. 1978. Production .3. Ali, A. D., Reagan, I. E., Flynn, J. L. Ecology of Ants and Termites. Cam- 1984. Influence of selected weedy and bridge: CambridgeUniv. Press weed-free sugarcane habitats on diet 14. Brown, E. S. 1959. Immaturenutfall of composition and foraging activity of the coconuts in the SolomonIslands. I. Dis- imported fire ant (Hymenoptera:Formi- tribution of nutfall in relation to that of cidae). Environ. Entomol. 13:1037- Amblypelta and of certain species of 41 ants. Bull. Entomol. Res. 50:97-113 4. Apperson, F. S., Adams, C. T. 1983. 15. Brown, E. S. 1959. Immaturenutfall of Medical and agricultural importance of coconuts in the Solomon Islands. II. red imported fire ant. Fla. Entomol. Changes in ant populations, and their 66:121-26 relation to vegetation. Bull. Entomol. 5. Bakri, A. H., Asid, M., Redshaw,M. J. Res. 50:523-58 1986. PemberantasanHelopeltis secara 16. Bruneau de MirE, P. 1969. Une fourmie terpadu dengan penggunaan semut utilisEe au Cameroundans la lutte contra hitam dan bahan kimia pada tanaman des mirides du cacaoyer Wasmanniaau- coklat di Sumatera Utara. Medan: Temu ropunctata Roger. Cafe, Cacao, The llmiah Entomologi Perkebunan In- 13:209-12 donesia. 11 pp. 17. Carroll, C. R., Janzen, D. H. 1973. 6. Baloch, G. M. 1973. Natural enemies of Ecologyof foraging by ants. Annu. Rev. Axiagastuscambelli Distant (I-lemiptera: Ecol. System. 4:231-57 Pentatomidae)on the Gazelle Peninsula, 18. Carroll, C. R., Risch, S. J. 1983. Tropi- NewBritain. Papua NewGuinea Agric. cal annual cropping systems: ant ecolo- J. 24:41-45 gy. Environ. Manage. 7:51-7 7. Beattie, A, 1985. The Evolutionary 19. Cherix, D. 1980. Note prEliminaire sur Ecology of Ant-Plant Mutualisms. New la structure, la phenologieet le regime York: Cambridge Univ. Press. 182 pp. alimentaire d’une super-colonie de For- 8. Behrndt, G. 1933. Die Bedentung der mica lugubris Zett. lnsectes Soc. Roten Waldameisebei Forleulenkalami- 27:226--36 t~iten. Z. Forst. Jagdwes. 65:479-98 20. Clark, D. B., Guayasamin, C., Pazmio 9. Behrndt, G. 1934. Einige Beobachtun- no, O., Donoso, C., Paez de Villacis, gen fiber die Bedentung von Formica Y. 1982. Wasmannia auropunctata: rufa und F. fusca bei Forieulenkal- autoecologyand effects on ant diversity amitaten. Forstarchiv 10:289-94 and distribution on Santa Cruz Island, 10. Betrem, J. G. 1948. Enkele grepen uit Galapagos. Biotropica 14:196-207 de biocenose van de cacao. Tijdschr. 21. Cotti, G. 1963. Bibliografia ragionata Entomol. 89:112-15 1930-1961 del gruppo Formica rufa in 11. Bonder, G. 1939. Insectos daninhos e italiano, deutsch, englisch. Rome: Annual Reviews www.annualreviews.org/aronline

498 WAY & KHOO

Ministero dell’agricoltura e delle for- 36. Giesberger, G. 1940. Eenige waame- este, Collana Verde No. 8. 413 pp. mingen over de aantasting van cacao 22. Delabie, J. H. C. 1990. The ant prob- door Helopeltis. Arch. Koffiecult. In- lems of cocoa farms in Brazil. See Ref. dones. 14:44-99 162, pp. 555-69 37. Giesberger, G. 1983. Biological control 23. E1-Haidari, H. S. 1981. The use of pred- of the Helopeltis pest of cocoa in Java. ator ants for the control of date palm In Cocoa Research in Indonesia 1900- insect pests in the YemenArab Repub- 1950, ed. H. Toxopeus, P. C. Wessel, lic. Date PalmJ. 1 : 129-30 2:91-180. Wageningen: Am. Cocoa 24. Esquival, R. E. A. 1983. Effective con- Res. Inst. and Int. Office of Cocoaand trol of the giant mothborerCastnia licus Chocolate (Drury) in Panama,utilising biological- 38. Girling, D. J. 1978. The distribution and cultural methods. Entomol. News Int. biology of Eldana saccharina (Lepidop- Soc. Sugar Cane Technol. 14:6--7 tera, ) and its relationship to 25. Faeth, S. H. 1980. Invertebrate preda- other stem borers in Uganda. Bull. En- tion of leaf miners at low densities. tomol. Res. 68:471-88 Ecol. Entomol. 5:111-14 39. Godfret, K. E., Whitcomb, W. H., 26. Fataye, A., de Taffin, G. 1989. Lutte Stimal, J. L. 1989. Arthropodpredators integrde contre Pseudotheraptus de- of velvet bean caterpillar Anticarsia vastans et especes voisines. Oleagineux gemmatalis Hubner (Lepidoptera: Noc- 44:525-30 tuidae), eggs and larvae. Environ. En- 27. Fillman, D. A., Sterling, W. L. 1983. tomol. 18:118-23 Killing power of the red imported fire 40. Godzifiska, E. J., Kieruzel, M., Korc- ant (Hym.: Formicidae): a key predator zyfiska, J. 1990. Predation of ants of the of the boll weevil (Col.: ). genus Formica L. (Hymenoptera, For- Entomophaga 28:339--44 micidae) on Colorado beetles, Leptino- 28. Fillman, D. A., Sterling, W. L. 1985. tarsa decemlineata Say. (Coleoptera, Inaction levels for the red imported fire Chrysomelidae). Memorabilia Zool. ant, Solqnopsis invicta (Hym.: Formici- 44:47-53 dae): a prddator of the boll weevil, An- 41. Gosswald, K. 1951. Die rote Walda- thonomusgrandis (Col.: Curculionidae). meise im Dienste der Waldhygiene. For- Agric. Ecosyst. Environ. 13:93 102 stwirtschaftliche Bedeutuna, Nutzuna, 29. Finnegan, R. J. 1971. An appraisal of Lebensweise, Zucht, Vermehrung und indigenousants as limiting agents of for- Schutz. Luneburg: Kinau-Verlag. 160 est pests in Quebec. Can. Entomol. PP. 103:1489-93 42. Gosswald, K. 1956. Neue Effahrungen 30. Finnegan, R. J. 1974. Ants as predators tiber Einwirkung der roten Waldameise of forest pests. Entomophaga Mere. auf den Massenwechselvon Schadinsek- Hors Ser. 7:53-59 ten sowie einige methodisehe. Ver- 31. Finnegan, R. J. 1975. Introduction of a besserungen bei ihrem praktischen Ein- predaceous red wood ant, Formica satz. Proc. lOth Int. Congr. Entomol. lugubris (Hymenoptera: Formicidae), 4:567-71. Montreal: Int. Congr. En- from Italy to Eastern Canada. Can. En- tomol. tomol. 107:1271-74 43. Gosswald, K. 1989. Die Waldemeise. 32. Fittkau, E. J., Klinge, H. 1973. On Band 1. Biologische Grundlagen, Okol- biomassand trophic structure of the cen- ogie und Verhalten. Wiesbaden: Aula- tral Amazonianrain forest ecosystem. Verlag. 660 pp. Biotropica 5:2-14 44. Gosswald, K. 1990. Die Waldameise. 33. Fuller, B. W., Reagan, T. E. 1988. Band 2. Die Waldemeise im Okosystem Comparativepredation of the sugarcane Wald, ihr Nutzen und ihre Hege. Wies- borer (Lepidoptera: Pyralidae) on sweet baden: Auta-Verlag. 510 pp. and sugarcane. J. Econ. En- 45. Gotwald, W. H. 1986. The beneficial tomol. 81:713-17 economicrole of ants. In EconomicIm- 34. Garcia, C. E. 1935. A field study of the pact and Control of Social Insects, ed, citrus green bug, Rhynchocoris serratus S. B. Vinson, pp. 290-313. NewYork: Donovan. Philipp. J. Agric. 6:311- Praeger 25 46. Gravena, S., Pazetto, J. A. 1987. Preda- 35. Gasogo, A. 1982. Etat des connais- tion and parasitism of cotton leafworm sances et observations complementaires eggs, Alabama argillacea (Lep.: Noc- sur Eldana saccharina Walker (Lep., tuidae). Entomophaga32:241~-8 Pyralidae) mineuse de tiges de gra- 47. Greathead, D. J. 1976. A Review of min6es. Z. Angew. Entomol. 93:365- Biological Control in Western and 78 Southern Europe. Tech. Commun. Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 499

Commonw.Inst. of Biol. Control, No. 62. Jaffr, K., Teblante, P. A., Sanchez, P. 7. Farnham: CIBC. 182 pp. 1986. Ecologia de Formicidaeen planta- 48. Greenslade, P. J. M. 1971. Interspecific ciones de cacao en Balovento, Vene- competition and frequency changes zuela. Rev. Theobroma 16:649-97 amongants in Solomon Islands coconut 63. Jolivet, P. 1986. Les Fourmis et les plantations. J. Appl. Ecol. 8:323~,9 Plantes. Paris: Bombeeet Foundation 49. Greenslade, P. J. M. 1972. Comparative Singer Polignac. 254 pp. ecology of four tropical ant species. In- 64. Jones, C. G., Whitman, D. W., Comp- sectes Soc. 19:195-212 tom, S. J., Silk, P. J., Blum, M. S. 50. Gridina, T. I. 1990. Influence of Formi- 1989. Reduction in diet breadth results ca polyctena Foerst. (Hymenoptera, in sequestration of plant chemicals and Formicidae)on the distribution of preda- increases efficacy of chemicaldefense in tory arthropods in forest ecosystems. a generalist grasshopper. J. Chem.Ecol. Memorabilia Zool. 44:21-36 15:1811-22 51. Haines, I. H., Haines, J. B. 1978. Col- 65. Jones, D., Sterling, W. L. 1979. Manip- ony structure, seasonality and food re- ulation of red importedfire ants in a trap quirementsof the crazy ant, Anoplolepis crop for boll weevil suppression. En- Iongipes (Jerd.), in the Seychelles. Ecol. viron. Entomol. 8:1073-77 Entomol. 3:109-18 66. Julia, J. F. 1978. La Punaise du coco- 52. Haines, I. H., Haines, J. B. 1978b. Pest tier: Pseudotheraptus sp. ll--Mrthode status of the crazy ant, Anoplolepislon- de lutte intrgrde en Crte d’Ivoire. gipes (Jerdon) (Hymenoptera: Formici- Oldagineux 33:113-18 dae) in the Seychelles. Bull. Entomol. 67. Julia, J. F. 1980. Surveillence sanitaire Res. 68:627-38 des cocoteraies adultes en de l’Ouest I~ 53. Heads, P. A., Lawton, J. H. 1985. Contrbles ordinaires. Ol~agineux Bracken, ants and extrafloral nectaries. 35:247-53 III. Howinsect herbivores avoid ant pre- 68. Julia, J. F. 1980. Surveillence sanitaire dation. Ecol. Entomol. 10:29-42 des cocoteraies adultes en Afrique de 54. Hensley, S. D., Long, W. H., Roddy, l’Ouest lI--Contrrles sprciaux. L. R., McCormick, W. J., Concienne, Ol~agineux 35:305-9 E. J. 1961. Effect of insecticides on the 69. Julia, J. F., Mariau, D. 1978. La predacious fauna of Louisiana punaise du cocotier: Pseudotheraptus sugarcane fields. J. Econ. Entomol. sp. en Crte d’Ivoire. I. Etudes prr- 54:146-49 alables ~ la mise au point d’une m~thode 55. Higashi, S., Yamanchi, K. 1979. In- de lutte intrgrre. Oleagineux 33:65- fluence of a supercolonial ant Formica 75 (Formica) yessensis Forel on the dis- 70. Jutsum, A. R., Cherrett, J. M., Fisher, tribution of other ants in Ishikari Coast. M. 1981. Interactions between the fauna Jpn. J. Ecol. 29:257-64 of citrus trees in Trinidad and the ants 56. Hrlldobler, B. 1979. Territories of the Atta cephalotes and Azteca sp. J. Appl. African weaver ant (Oecophylla longi- Ecol. 18:187-95 noda [Latreille]). Z. Tierpsychol. 71. Kajat, A., Breymeyer, A., Petal, J. 51:201-13 1971. Productivity investigation of two 57. Hrlldobler, B. 1983. Territorial be- types of meadowsin the Vistula Valley. haviour in the green tree ant (Oecophylla XI. Predatory arthropods. Ekol. Pol. smaragdina). Biotropica 15:241-50 19:223-33 58. l-Irlldobler, B., Wilson, E. O. 1978. 72. Khoo, K. C., Chung, G. F. 1989. Use The multiple recruitment systems of the of the black cocoa ant to control mirid African weaver ant Oecophylla longino- damage in cocoa. Plant. Kuala Lumpur da (Latreille) (Hymenoptera: Formici- 65:370-83 dae). Behav. Ecol. Sociobiol. 3:19-60 73. Korytkowski, G., Ruiz, A. 1979. El 59. H/511dobler, B., Wilson, E. O. 1990. Barreno de los racimos de la palma The Ants. Berlin: Springer-Verlag. 732 aceitera, Castnia daedalus (Cramer) PP. Lepidopt.: Castniidae en la plantacion de 60. I-luang, H. T., Yang, P. 1987. The an- Tocache--Peru. Rev. Peru. Entomol. cient cultured citrus ant. Biosciences 22:49-62 37:665-71 74. Krumschmidt, W. 1974. Praktische 61. Jaffr, K., Mauleon, H., Kermarrec, A. Erfahrungen in der Waldemeisenhege. 1990. Predatory ants of Diaprepes Allg. Forst. Jagdztg. 145:71 77 abbreviatus (Coleoptera: Curculionidae) 75. Lee, J. H., lohrtson, S. J., Wright, U. in citrus groves in Martinique and L. 1990. Qualitative survivorship Guadeloupe, F. W. I. Fla. Entomol. analysis of the velvetbean caterpillar 73:684-87 (Lepidoptera: Noctuidae) pupae in soy- Annual Reviews www.annualreviews.org/aronline

500 WAY & KHOO

bean fields in Louisiana. Environ. En- predation in the red woodant (Formica wmol. 19:978-86 polyctena Forst.)Neth. J. Zool. 29:451- 76. Leston, D. 1973. The ant mosaic-- 620 tropical tree crops and the limiting of 90. Macfarlane, R. 1985. Annual Report pest and diseases. PANS19:311-41 1984. Honiara: Res. Dept., Agric. Div., 77. Leston, D. 1978. A neotropical ant SolomonIslands Ministry of Agriculture mosaic. Ann. Entomol. Soc. Am. and Lands. 27 pp. 71:649-53 91. Macfarlane, R., Jackson, G. V. H., 78. Letourneau, D. K. 1983. Passive Morten, K. D. 1976. Die-back of Eu- aggression: Analternative hypothesis for calyptus in the Solomon Islands. Com- the Piper-Pheidole association. Oeco- monw. For. Rev. 55:133-39 Iogia 60:122-26 92. Majer, J. D. 1972. The ant mosaic in 79. Lever, R. J. A. W. 1933. Notes on two Ghanacocoa farms. Bull. Entomol. Res. hemipterous pests of the coconut in the 62:151-60 British Solomon Islands. Agric. Gaz. 93. Majer, J. D. 1974. The use of ants in an Br. Solomon Isl. 1:2-6 integrated control scheme for cocoa. 80. Levert, Ph. 1940. Het mier-luis- Proc. 4th Conf. West African Cocoa En- complex bij cacao en verdere gegerens tomologists, pp. 181-90. Legon, Ghana: over Helopeltis-aantasting. Arch. Kof- Dept. Zool., Univ. Ghana fiecult. Indones. 14:1-43 94. Majer, J. D. 1976. The maintenance of 81. Lewis, T., Cherrett, J. M., Haines, J., the ant mosaic in Ghanacocoa farms. J. Mathias, P. L. 1976. The crazy ant (An- Appl. Ecol. 13:123-44 oplolepis longipes Jerd.) (Hymenoptera, 95. Majer, J. D. 1976. The influence of ants Formicidae)in Seychelles and its chemi- and ant manipulation on the cocoa fama cal control. Bull. Entomol. Res. 66:97- fauna. J. Appl. Ecol. 13:157-75 111 96. Majer, J. D 1986. Utilising economical- 82. Loehr, B. 1990. The pugnacious antAn- ly b6tieficial ants. See Ref. 168, pp. oplolepis custodiens and its relation to 3 lzl-31 coconut palms in Tanzania. Annual Re- 97. Majer, J. D. 1986. Ant manipulation in port 1989-90 NCDP,pp.83-93. Dares agro- and forest-ecosystems. In Eco- Salaam, Tanzania: Natl. Coconut Dev. nomic Impact and Control of Social In- Prog. sects, ed. M. D. Breed, C. D. Michener, 83. Loehr, B., Zerhusen, D., Raschid, M. H. E. Evans, pp.90-97. Boulder: West- 1990. Use of Amdroant baits against view Pheidole megacephalaand related spe- 98. Margalef, R. 1968. Perspectives in Eco- cies. Annual Report 1989-90 NCDP, logical Theory. Chicago: Univ. Chicago pp.52-61. Dares Salaam, Tanzania: Press. 111 pp. Natl. Coconut Dev. Prog. 99. Markin, G. P., Dillier, J. H., Collins, 84. Lofgren, C. S. 1986. The economic im- H. L. 1973. Growth and development of portance and control of imported fire colonies of the red imported fire ant ants in the United States. See Ref. 168, Solenopsis invicta. Ann. Entomol. Soc. pp. 227-56 Am. 66:803-9 85. Lofgren, C. S. 1986. History of im- 100. McDaniel, S. G., Sterling, W. L. 1979. ported fire ants in the United States. See Predator determination and efficiency on Ref. 86a, pp. 36-47 Heliothis virescens eggs on cotton using 86. Lofgren, C. S., Banks, W. A., Glancey, 32p . Environ. Entomol. 8:1083 87 B. M. 1975. Biology and control of im- 101. McDaniel, S. G., Sterling, W. L. 1982. ported fire ants. Annu. Rev. Entomol. Predation of Heliothis virescens (F.) 20:1-30 eggs on cotton in east Texas. Environ. 86a. Lofgren, C. S., Vander Meer, R. K., Entomol. 11:60-66 eds. 1986. Fire Ants and Leaf-Cutting 102. McGregor, A. J., Moxon, J. E. 1985. Ants. Boulder/London: Westview Potential for biological control of tent 87. Long, W. H., Concienne, E. A., Con- building species of ants associated with cienne, E. J., Dobson, R. N., Newsom, Phytophthora palmivora pod rot of L. D. 1958. Fire ant eradication in- cocoa in Papua NewGuinea. Ann. Appl. creases damageby the sugarcane borer. Biol. 107:271-77 Sugar Bull. 37:62~63 103. McNeil,J. N., Delisle, J., Finnegan, R. 88. Lubin, Y. D. 1984. Changes in the na- J. 1978. Seasonal predatory activity of tive fauna of the Galapagos Islands the introduced red wood ant Formica following invasion by the little red fire lugubris (Hymenoptera: Formicidae) ant, Wasmanniaauropunctata. Biol. J. Valcartier, Quebec, in 1976. Can. En- Linn. Soc. 21:229-42 tomol. 110:85-90 89. Mabelis, A. A. 1979. Woodant wars: 104. Messina, F. J. 1981. Plant protection as the relationship between aggression and a consequence of an ant-membracid Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 501

mutualism: interactions on Goldenrod du group Formica rufa pour la defense (Solidago sp.). Ecology 62:1433-40 biologique des forets. Proceedingsof the 105. Morrill, W. L. 1974. Production and meeting of the working groups on For- flight of alate red imported fire ants. mica rufa and vertebrate predators of Environ. Entomol. 3;265-71 insects. Bull. WestPalearctic Reg. Sect. 106. Muller, H. 1956. Konnen Honigtau Int. Org. Biol. Control 2:135-59. Va- liefernde Baumlause (Lachnidae) ihre renna, Italy: West Palearctic Regional Wirtspflanzen sch~idigen? Z. Angew. Section of the IOBC Entomol. 39:168-77 118. Petal, J. 1978. The role of ants in eco- 107. Murray, G. H. 1937. Outbreak Pro- systems. See Ref. 13a, pp. 293-325 mecotheca antiqua Lindenhafen Es- 119. Phillips, J. S. 1940. Immaturenutfall of tate. NewGuinea Agric. Gaz. 3:1-2 coconuts in the SolomonIslands. Bull. 108. Needham,J. 1986. Science and Civilisa- Entomol. Res. 31:295-316 tion in China, Vol. VI, Biology and 120. Pisarski, B. 1978. Comparisonof vari- Biological Technology, Part 1: Botany. ous biomes. See Ref. 13a, pp. 326-31 Cambridge: CambridgeUniv. Press. 718 121. Pontin, A. J. 1960. Field experimentson pp- colony foundation by Lasius niger (L.) 109. Nickerson, J. C., Kay, C. A. R., Busch- and L. flavus (F.) (Hym.: Formicidae). man, L. L., Whitcomb, W. H. 1977. lnsectes Soc. 7:227-30 Thepresence of Spissistilus festinus as a 122. Pontin, A. J. 1961. Population stabilisa- factor affecting egg predation by ants in tion and competition between the ants soybeans. Fla. Entomol. 60:193-99 Lasiusflavus (F.) and L. niger (L.). 110. O1oo, G. W. 1989. The role of local Anim. Ecol. 30:47-54 natural enemies in population dynamics 123. Reagan, T. E. 1986. Beneficial aspects of Chilo partellus (Swinh.). (Pyralidae) of the imported fire ant: a field ecology under subsistence farming conditions in approach. See Ref. 86a, pp. 58-71 Kenya. Insect Sci. Appl. 10:243-51 124. Reagan, T. E., Coburn, G., Hensley, S. 111. O1oo, G. W., Odega, K. 1990. The in- D. 1972..~Effects of Mirexon the arthro- cidence of Chilo partellus (Swinh.) pod fauna of a Louisiana sugarcane (Pyralidae) and the contribution of nat- field. Environ. Entomol. 1:588-91 ural enemies to its mortality under in- 125. Reilly, J. J., Sterling, W. L. 1983. In- tercropping systems in Kenya. Trop. terspecific association between the red Pest Manage. 36:244-48 imported fire ant (Hymenoptera:Formi- 112. O’Sullivan, D. F. 1973. Observations cidae), aphids, and somepredaceous in- on the coconut spathe bug Axiagastus sects in a cotton agroecosystem. En- cambelli Distant (: Pentatomi- f, iron. Entomol.12:541-45 dae) and its parasites and predators in 126. Risch, S. J. 1981. Ants as important Papua New Guinea. Papua New Guinea predators of rootwormeggs in the neo- Agric. J. 24:79-86 tropics. J. Econ. Entomol. 74:88-90 113. Overal, W. L., Posey, P. A. 1984. Uso 127. Risch, S. J., Carroll, C. R. 1982. The de formigas do genero Azteca por con- ecological role of ants in two Mexican trole de saavas entre os indios kaiapos agroecosystems. Oecologia 55:114-19 do Brasil. Attini 16:2 128. Risch, S. J., Carroll, C. R. 1982. 114. Pascovici, V. D. 1979. Esp~ces du Effects of a keystone predaceous ant, groupe Formica rufa L. de Roumanieet Solenopsis geminata, on arthropods in a leur utilisation dans la lutte contre les tropical agroecosystem. Ecology ravageursforesti~res. Proceedingsof the 63:1979-83 meeting of the working groups on For- 129. Robertson, H. G. 1985. Egg predation mica rufa and vertebrate predators of by ants as a partial explanation of the insects. Bull. West Palearctic Reg. Sect. difference in performanceof Cactoblas- Int. Org. Biol. Control 2:111-34. Va- tis cactorum on cactus weeds in South renna, Italy: West Palearctic Regional Africa and Australia. Proc. 6th Int. Section of the IOBC Syrup. Biol. Control of Weeds, pp. 83- 115. Paulson, G. S., Akre, R. D. 1991. 88. Ottawa: Agric. Canada Evaluating the effectiveness of ants as 130. Roche, R. 1977. Comunication pre- biological control agents of pear psylla liminar sobre la hormiga Tetramorium (Caeopsylla pyricola Foerster). J. Econ. guineense, control biologico del picudo Entomol. In press negro del platano. Rev. Agric. Cuba. 116. Pavan, M. 1959. Attivita per la lotta 8:35-37 biologica con formiche del gruppo For- 131. Roepke, W. 1916. Het Helopeltis- mica rufa contro gli insetti dannosi aile vraagstuk, in het bijzonder met betrek- foreste. Min. Agric. For. Coll. Verde king tot cacao. Meded. Proefsm. Mid.- 4:1-80 Java 21:1-40 117. Pavan, M.1979. Utilisation des fourrnis 132. Room, P. M. 1971. The relative dis Annual Reviews www.annualreviews.org/aronline

502 WAY & KHOO

tribution of ant species in Ghana’scocoa 148. Steyn, J. J. 1954. The pugnaceous ant farms. J. Anim. Ecol. 40:735-51 (Anoplolepis custodiens Smith) and its 133. Room,P. M. 1973. Control by ants of relation to the control of citrus scales at pest situations in tropical tree crops; a Letaba. Mem. Entomol. Soc. S. Africa strategy for research and development. No. 3. 96 pp. Papua NewGuinea Agric. J. 24:98-103 149. Strickland, A. H. 1951. The entomology 134. Room, P. M. 1975. Diversity and of swollen shoot of cacao. I. The insect organisation of the ground foraging ant species involved, with notes on their bi- faunas of forest, grassland and tree crops ology. Bull. Entomol Res. 41:725-48 in Papu~ NewGuinea. Aust. J. Zool. 150. Strickland, A. H. 1951. The entomology 23:71-89 of swollen shoot of cacao. II. The bio- 135. Room, P. M., Smith, E. S. C. 1975. nomics and ecology of the species in- Relative abundance and distribution of volved. Bull. Entomol. Res. 42:65-103 insect pests, ants and other components 151. Sturm, M. M., Sterling, W. L. 1990. of the cocoa ecosystem in Papua New Geographical patterns of boll weevil Guinea. J. Appl. Ecol. 12:31-46 mortality: observations and hypothesis. 136. Saks, M. E., Carroll, C. R. 1980. Ant Environ. Entomol. 19:59-65 foraging activity in tropical agro- 152. Sudd, J. H., Douglas, J. M., Gaynard, ecosystems. Agro-Ecosystems 6:177-88 T., Murray, M., Stockdale, J. M. 1977. 137. Sato, H., Higashi, S. 1987. Bionomics The distribution of woodant (Formica of Phyllonorycter (Lepidoptera, Gracil- lugubris Zetterstedt) in a northern En- lariidae) on Quercus.II. Effects of ants. glish forest. Ecol. Entomol. 2:301-13 Ecol. Res. 2:53--60 153. Szent-lvany, J. J. H. 1961. Insect pests 138. Schemske, D. W. 1980. The evolution- of Theobromacacao in the territory of ary significance of extrafloral nectar pro- Papua NewGuinea. Papua New Guinea duction by Costus woodsonii (Zingiber- Agric. J. 13:127~,7 aceae); an experimental analysis of ant 154. Taley, Y. M. 1976. Tapinoma indicum protection. J. Ecol. 68:959-67 Forel (Formicidae: Hymenoptera)a new 139. Silva, P. 1955. A formiga de enxerto. predatory ant of jowar midge Contarinia Boletim de Divulgacao no. 1. Livraria sorghicola (Cecidomyiidae: Diptera). Duas Americas. Bahia, Brazil: Instituto Cecidol. lndica 11:77-9 de Cacau de Bahia. 21 pp. 155. Taylor, T. H. C. 1937. The Biological 140. Smith, E. S. C. 1981. An integrated Control of an Insect in Fiji. London: control scheme for cocoa pests and dis- Imperial Institute of Entomology. 239 eases in Papua NewGuinea. Trop. Pest. PP. Manage. 27:351-59 156. Torrend, G. 1919. As molestias dos 141. Southwood,T. R. E., Way, M. J. 1970. cacaueiros em ilheos (Bahia). Broteria Ecological background to pest manage- Portugal 16:26z1~78 ment. In Concepts of Pest Management, 157. Travan, J. 1987. Herk6mmliche und ed. R. L. Rabb, F. E. Guthrie, pp. 6-28. neuere Methodender Kunstlichen Wald- Raleigh: North Carolina State Univ. ameisen. Waldhygiene 17:85-92 142. 8pektor, M. R. 1975. Operation "Ant" 158. Tschinkel, W. R. 1986. The ecological in the Uka-aine. Zttshch. Rast. 7:40-42 nature of the fire ant: some aspects of 143. Stapley, J. H. 1973. Insect pests of colony function and some unanswered coconuts in the Pacific Region. Outlook questions. See Ref. 86a, pp. 72-87 Agric. 7:211-17 159. Tschinkel, W. R., Howard, D. F. 1983. 144. Stapley, J. H. 1980. Coconutleaf beetle Colony founding by pleometrosis in the (Brontispa) in the Solomons. Alafua fire ant, Solenopsis invicta. Behav. Agric. Bull. 5:17-22 "Ecol. Sociobiol. 12:103-13 145. Sterling, W. L. 1978. Fortuitous biolog- 160. Ulloa-Chalon, P., Cherix, D. 1990. The ical suppressionof the boll weevil by the little fire ant, Wasmanniaauropunctata red imported fire ant. Environ. Entomol. (R.) (Hymenoptera: Formicidae). 7:564--68 Ref. 162, pp. 281-89 146. Sterling, W. L., Dean, D. A., Fillman, 161. Van der Goot, P. 1917. De zwarte D. A., Jones, D. 1984. Naturally occur- cacao-mier (Dolichoderus bitubercula- ring biological control of the boll tus Mayr.) en haar beteenkenis voor de weevil, Col.: Curculionidae. Entomo- cacao-cultuur op Java. Meded. Proefstn. phaga 29:1-9 Mid.-Java 25:1-142 147. Sterling, W. L., Jones, D., Dean, D. A. 162. Vander Meer, R. K., Jaffe, K., Cedeno, 1979. Failure of the red importedfire ant A., eds. 1990. Applied Myrmecology:A to reduce entomophagous insect and World Perspective. Boulder/Oxford: spider abundancein a cotton, agroecosys- Westview. 741 pp. tem. Environ. Entomol. 8:976-81 163. Vanderplank, F. L. 1959. Studies on the Annual Reviews www.annualreviews.org/aronline

ANTS AND PEST MANAGEMENT 503

coconut pest Pseudotheraptus wayi in relation to biological control of the Brown (Coreidae) in Zanzibar. III. coconut caterpillar, Opisina arenosella selective residual insecticidal formula- Walker (Lepidoptera: Xyloryctidae), tion and its effects on the ecologyof the . Bull. Entomol. Res. 79:219- insect. Bull. Entomol. Res. 50:151- 33 177. Way, M. J., Khoo, K. C. 1989. Rela- 164. Vanderplank, F. L. 1960. The biono- tionships between Helopeltis theobro- mics and ecology of the red tree ant, macdamage and ants with special refer- Oecophyllasp. and its relationship to the ence to Malaysian cocoa smallholdings. coconut bug Pseudotheraptus wayi J. Plant Prot. Tropics 6:1-11 Brown (Coreidae). J. Anita. Ecol. 178. Way, M. J., Khoo, K. C. 1991. Colony 29:15-33 dispersion and nesting habits of Dolicho- 165. Van Hamburg,H., Hassell, M. P. 1984. derus thoracicus and Oecophylla smar- Density dependence and the augmenta- agdina (Hymenoptera: Formicidae) tive release of egg parasitoids against relation to their success as biological graminaceous stalkborers. Ecol. En- control agents on cocoa. Bull. Entomol. tomol. 9:101-8 Res. 81: In press 166. Varela, A. M. 1990. Workon the biolo- 179. Wellenstein, G. 1952. Zur Ernahrung- gy of . Annual Re- sbiologie der Roten Waldameise. Z. port 1989-90, NCDP,pp. 71-82. Dares Pflanzenkr. Pflanzenschutz 59:430-51 Salaam, Tanzania: Natl. Coconut Dev. 180. Wellenstein, G. 1954. Was krnnen wir Prog. yon der Roten Waidameise im Forsts- 167. Vello, F., Magalhaes, W. S. 1971. Es- chutz erwatten? Beitr. Entomol. 4:117- tudos sobre a participacao da formiga 38 cocarema(Azteea ehartifex spiriti Ford) 181. Wellenstein, G. 1954. Die insektenjagel ha polinizacao do cauaueiro na Bahia. der Roten Waldameise. Z. Angew. En- Rev. TheobromaBrazil 1:29-42 tomol. 36:185-217 168. Vinson, S. B., ed. 1986. Economic Im- 182. Wellenstein, G. 1959. Mrglichkeiten pact and Control of Social lnseets. New und Grenzen des Einsatzes von Krank- York: Praeger. 421 pp. heitserregern, Nutzinsekten und Vrgeln 169. Vinson, S. B. Oreenberg, L. 1986. The im praktischen Forschutz. Forstwiss. biology, physiology and ecology of im- Centralbl. 75:150-66 ported fire ants. See Ref. 168, pp.193- 183. Wellenstein, G. 1967. Zur Frage der 226 Standortsanspriiche Hiigelbanender 170. Vofite, A. D. 1935. Cryptorrhynehus Waldameisen(F. rufa Gruppe). Z. An- gravis F. und die Ursachen seiner Mas- gew. Entomol. 54:13%66 senvermehrung in Java. Arch. Neerl. 184. Weseloh, R. M. 1989. Simulation of Zool. 2:112-42 predation by ants based on direct .171. Way, M. J. 1953. Studies in Theraptus observations on gypsy moth larvae. sp. (Corcidac), the cause of gumming Can. Entomol. 121:1069-76 disease of coconutsin East Africa. Bull. 185. Whitcomb, W. H., Denmark, H. A., Entomol. Res. 44:657-68 Bhatkar, A. P., Greene, G. L. 1972. 172. Way, M. J. 1953. The relationship be- Preliminary studies on the ants of Flor- tweencertain ant species with particular ida soybean fields. Fla. Entomol. 55: reference to biological control of the 129-42 coreid, Theraptus sp. Bull. Entomol. 186. Whittaker, J. B., Warrington, S. 1985. Res. 44:66%91 An experimental field study of different 173. Way, M. J. 1954. Studies on the life levels of insect herbivory induced by history and ecology of the ant Oecophyl- Formica rufa predation on sycamore la longinoda Latreille. Bull. Entomol. (Acer pseudoplatanus) III. Effects on Res. 45:93-112 tree growth. J. Appl. Ecol. 22:797-811 174. Way, M. J. 1954. Studies on the 187. Wilson, E. O. 1959. Some ecological association of the ant Oecophyllalongi- characteristics of ants in NewGuinea noda (Latr.) (Formicidae) with the scale rain forests. Ecology 40:437-47 insect Saissetia zanzibarensis Williams 188. Wilson, E. O. 1971. The Insect Societ- (Coccidae). Bull. Entomol. Res. 45: ies. Cambridge,MA: Be ..ll~nap. 548 pp. 113-34 189. Wuorenrinne, H. 1975. Uber die Not- 175. Way, M. J. 1963. Mutualism between wendigkeiten und die Mrglichkeiten des ants and honeydew-producing Homop- Waldameisenschutzes in Finnland. tera. Annu. Rev. Entomol. 8:307-44 Waldhygiene 11:48-50 176. Way, M. J., Cammell, M. E., Bolton, 190. Yang, P. 1982. Biology of the yellow B., Kanagaratnam, P. 1989. Ants citrus ant, Oecophylla smaragdina and (Hymenoptera:Formicidae) as egg pred- its utilisation against citrus insect pests. ators of coconut pests, especially Acta Sci. Nat. Univ. Sunyatseni 3:102-5