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Biological Control of Insect Pests: Southeast Asian Prospects - EcoPort

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4.12 Nezara viridula 217<br />

Doubt has been cast (Clarke 1990) both on the policy and effectiveness<br />

<strong>of</strong> introducing strains <strong>of</strong> T. basalis from different regions having differing<br />

environmental conditions. This practice has either led in Australia to<br />

effective biological control <strong>of</strong> N. viridula extending into additional<br />

environments or, alternatively, the initial genetic make-up <strong>of</strong> T. basalis has<br />

steadily undergone changes to allow progressive adaptation to new<br />

environments. It is possible that T. basalis consists <strong>of</strong> a complex <strong>of</strong> sibling<br />

species but, if not, it would be surprising if T. basalis has remained a<br />

homogenous species worldwide. Johnson (1985) found that American<br />

specimens <strong>of</strong> T. basalis showed much less morphological variation than<br />

those <strong>of</strong> Africa suggesting an African origin for the species. Furthermore,<br />

Handley (1975) reported that Australian T. basalis females would not mate<br />

with American males, although Powell and Shepherd (1982) found that<br />

reproductive isolation did not occur within any <strong>of</strong> 3 Australian strains<br />

examined; or between them and a strain from Florida. Nevertheless, the<br />

latter strain proved least fecund. Ferreira and Zamataro (1989) found no<br />

differences in reproductive capacity or longevity between an Australian and<br />

a Brazilian strain <strong>of</strong> T. basalis and Awan et al. (1989) concluded that Italian,<br />

French and Spanish populations consist <strong>of</strong> a single biotype, although several<br />

significant differences were observed in their biology. On the other hand,<br />

differences in courtship behaviour have been observed between different<br />

populations <strong>of</strong> T. basalis (Bin et al. 1988; Clarke and Walter 1992).<br />

However, it is not known whether any <strong>of</strong> these differences has any<br />

significance for biological control.<br />

Three other wasps have been introduced, Trissolcus mitsukurii (Japan<br />

1962), Telenomus chloropus (Japan 1962, Japan via USA 1980) and<br />

Ooencyrtus submetallicus (West Indies 1952Ð53). Only the former is<br />

believed to have become established but its impact has not been reported<br />

(Field 1984; J. Turner pers. comm. 1985).<br />

The only parasitoid reported from adult or nymphal N. viridula is the<br />

native tachinid Cylindromyia rufifemur (Cantrell 1984; Coombs and Khan<br />

1997). Three exotic species <strong>of</strong> parasitic tachinid fly have also been<br />

employed in attempts at biological control <strong>of</strong> Nezara viridula, Trichopoda<br />

pennipes from Florida, T. pilipes from the West Indies and Bogosia antinorii<br />

from Kenya. The Trichopoda species were introduced into Australia in the<br />

1940s and 1950s, but failed to become established (Wilson 1960). More<br />

recently the Trichopoda species were introduced into Western Australia<br />

from their native countries and also from Hawaii where they have been<br />

successfully established (Michael 1981). They have not become established<br />

in Australia. It is tempting to postulate that the pheromone blend secreted by<br />

Australian N. viridula does not attract Trichopoda pennipes and T. pilipes

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