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306 Biotechnological Approaches for Pest Management and Ecological Sustainability<br />

accidental release of transgenic insects in the environment. Extreme mobility, small size,<br />

and large numbers of insects that exist in laboratories the world over have a high probability<br />

of accidental escape of transgenic insects into the environment. Scant attention has<br />

been paid to monitoring and actual impact of accidental escapes.<br />

In general, transgenic insects have a reduced fi tness, but it may not be true in all cases.<br />

There are no established procedures in place to conduct risk assessment for transgenic<br />

insects, as the goal is to spread them as far as possible (Hoy, 2000). Insects with insecticide<br />

resistance traits might pose a threat to public health (Hoy et al., 1997). Each transgenic species<br />

should be evaluated on a case-by-case basis depending on whether an insect species<br />

is a pest or a benefi cial arthropod. Host/prey specifi city is usually important to ensure that<br />

arthropod biological control agents control the target pests. Changes in host specifi city of<br />

a vector insect or agricultural pest should be carefully evaluated. Host range or preference<br />

should be documented through laboratory or greenhouse no-choice tests. Temperature<br />

and relative humidity tolerances and diapause attributes often restrict geographical distribution<br />

of arthropods. Changes in responses to abiotic factors should be demonstrable with<br />

growth chamber and laboratory tests by comparing the responses of transgenic with those<br />

of the unmanipulated strains. Laboratory tests should also determine whether the trait is<br />

transmitted to the progeny. Likewise, genetic evaluations should determine whether the<br />

inserted gene(s) are maintained in their original insertion site. For this reason, it may be a<br />

good idea to avoid the use of transformation methods, such as transposable-element<br />

vectors, that could result in movement of the inserted DNA. Even a transposable-element<br />

vector lacking the transposase gene could possibly move if a transposase were supplied by<br />

a helper transposable element that was native to the engineered species. Likewise, it may<br />

be important to determine that the inserted gene cannot be transmitted to the pest species,<br />

particularly if it confers resistance to pesticides (Tiedje et al., 1989; Hoy, 1992b).<br />

Concerns have also been raised about the safety of classical biological control agents.<br />

The environmentalists are particularly concerned about the preservation of native fl ora<br />

and fauna (Howarth, 1991). The era of accepting classic biological control as environmentally<br />

risk free appears to have passed (Harris, 1985; Ehler, 1990; Hoy, 1992b). Protocols for<br />

evaluating the risks associated with releasing parasitoids and predators that have been<br />

manipulated with rDNA techniques do not currently exist, but will probably include, as a<br />

minimum, the questions or principles governing the release of genetically modifi ed living<br />

organisms (Tiedje et al., 1989; Hoy, 1990b, 1992b, 1995). Some of the concerns that need to be<br />

addressed are discussed below.<br />

Genetic Exchange with Natural Populations<br />

Genetic variation, in general, is much greater in natural populations than in transgenic<br />

insects. Mating between transgenic and wild populations would expose the transgenic<br />

insects to a range of genetic backgrounds that would allow for broad nonadditive effects.<br />

These interactions may alter vector competence and host range, and infl uence life history<br />

parameters by affecting survival and reproduction (Gubler, 1993). Novel traits may spread<br />

to a large geographical area in a short span of time (Daborn et al., 2002). The risks associated<br />

with accidental release of a transgene are largely associated with the nature of the<br />

transgene, the marker gene, and their expression patterns. Interspecifi c transfer of the<br />

transposable element mariner has been suggested for Drosophila and Zaprionus (Maruyama<br />

and Hartl, 1991), and the lepidopteran, H. cecropia (Lidholm, Gudmundsson, and Boman,<br />

1992). While the interspecifi c transfer of mariner is suspected only on the basis of DNA<br />

sequence similarities and no specifi c vector has been identifi ed, the data are consistent

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