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

Bt transgenic corn cultivation appears to have no signifi cant infl uence on the nematofauna,<br />

neither at the level of genus composition nor with regard to biodiversity (Manachini<br />

and Lozzia, 2002). Nevertheless, one region did have a change in trophic group composition:<br />

fungal feeding nematodes were more numerous in the soil with Bt corn, while in the fi eld<br />

with the isogenic hybrid, the bacterial feeders were higher than the Bt corn. The Cry1Ab<br />

protein had no consistent effects on nontarget organisms (earthworms, nematodes, protozoa,<br />

bacteria, fungi) in soil or in vitro. The Cry1Ab protein was not taken up from soil by<br />

non-Bt corn, carrot, radish, or turnip grown in soil in which Bt corn had been grown or<br />

into which biomass of Bt corn had been incorporated (Stotzky, 2004). No effects have been<br />

detected in culturable bacteria, fungi, protozoa, and nematodes from the Bt-maize fi elds<br />

(Saxena and Stotzky, 2001). Under fi eld conditions, the microfl ora of Bt transgenic potato<br />

plants has been observed to be minimally different from that of chemically and microbially<br />

treated commercial potato plants (Donegan et al., 1996). It is unlikely that expression<br />

of Bt and any other genes in transgenic plants would have an adverse effect on the soil<br />

microfl ora. There are no signifi cant differences in mortality or weight of the earthworm,<br />

Lumbricus terrestris L., after 40 days in soil planted with Bt maize or after 45 days in soil<br />

amended with Bt maize (Saxena and Stotzky, 2001). Toxin has been detected in the gut and<br />

casts of earthworms, but is cleared in two to three days after being placed in fresh soil.<br />

A 200-day study has been carried out to investigate the impact of Bt transgenic corn on<br />

immature and adult L. terrestris in the fi eld and in the laboratory. No lethal effects of transgenic<br />

Bt corn on immature and adult earthworms were observed (Zwahlen et al., 2003).<br />

Immature L. terrestris in the fi eld had a very similar growth pattern when fed either transgenic<br />

(Bt) or nontransgenic (non-Bt) corn litter. No signifi cant differences were observed in<br />

relative weights of L. terrestris adults fed on transgenic or nontransgenic corn during the<br />

fi rst 160 days in a laboratory trial, but after 200 days, the adult L. terrestris exhibited a<br />

weight loss of 18% when fed transgenic corn litter compared to a weight gain of 4% in<br />

those fed on nontransgenic corn. Further studies are necessary to see whether or not this<br />

difference in relative weight was due to the degradation of Cry1Ab toxin in corn residues<br />

(Zwahlen et al., 2003). Percentage infection of H. virescens larvae by Nomuraea rileyi (Farlon)<br />

was greater on Bt transgenic plants, and higher in the normal larvae than in Bt-resistant<br />

larvae, and might accelerate adaptation to Bt transgenic plants ( Johnson, Gould, and<br />

Kennedy, 1997).<br />

The proteinase inhibitor concentration in the transgenic plant litter after 57 days was<br />

0.05% of the sample at day 0, and was not detectable in subsequent sampling (Donegan<br />

et al., 1997). Although the carbon content of the transgenic plant litter was comparable to<br />

that of the parental plant litter on sample day 0, it became signifi cantly lower over time.<br />

Nematode populations in the soil surrounding the transgenic plant litter bags were greater<br />

than those in the soil surrounding parental plant litter bags and had a different trophic<br />

group composition, including a signifi cantly higher ratio of fungal feeding nematodes to<br />

bacterial feeding nematodes on sample day 57. In contrast, Collembola populations in the<br />

soil surrounding the transgenic plant litter bags were signifi cantly lower than in the soil<br />

surrounding parental plant litter bags, indicating that under fi eld conditions, the proteinase<br />

inhibitor remained immunologically active in buried transgenic plant litter for at<br />

least 57 days and that decomposing parental and transgenic plant litter differed in quality<br />

(carbon content) and in the response of exposed soil organisms (Collembola and nematodes)<br />

(Donegan et al., 1997). Susceptibility of Nosema pyrausta (Paillot)-infected European corn<br />

borer, O. nubilalis, to Bt formulation Dipel ES is greater than to the uninfected larvae. Dipel<br />

ES reduced N. pyrausta spore production in larvae feeding on diet containing Dipel ES,<br />

suggesting that Bt maize might have some adverse effects on the survival and continual

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