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

%mortality 100 ppm (cotton)<br />

100<br />

80<br />

60<br />

40<br />

20<br />

0<br />

Delhi Hyderabad Mansa Guntur Bapatla<br />

Population<br />

FIGURE 12.1 Variation in susceptibility of Helicoverpa armigera to Bacillus thuringiensis at different locations in<br />

India. (From Gujar, G.T. et al., 2000. Current Science 78: 995–1001. With permission.)<br />

have shown more than 16-fold resistance to Bt toxins (Karim and Riazuddin, 1999). Preadaptation<br />

of insects to various temperature regimes, differences in genetic make-up of<br />

populations, and use of xenobiotics might be responsible for variations in susceptibility of<br />

insects to B. thuringiensis (Broza, 1986; Chandrashekar et al., 2005).<br />

Extensive investigations on baseline susceptibility of H. armigera to Bt have been carried<br />

out in China (Zhao et al., 1996). Shen et al. (1998) reported that populations of H. armigera<br />

from Yanggu (Shadong), Handan (Hebei), Xinxian (Henan), Xiaoxian (Anhui), and<br />

Fengxian ( Jiangsu) were resistant to Bt as compared to the susceptible strain. Populations of<br />

H. armigera from Yanggu and Xinxian were also resistant to transgenic cotton. This variation<br />

in insect susceptibility was attributed to large-scale use of B. thuringiensis var. kurstaki,<br />

and signifi cant cultivation of transgenic cotton in China. Wu, Guo, and Nan (1999) reported<br />

100-fold variation in susceptibility of H. armigera from fi ve regions in China to Cry1Ac.<br />

Further studies on monitoring of insect susceptibility to Cry1Ac were carried out for the<br />

populations sampled from B. thuringiensis transgenic cotton fi elds by Wu, Guo, and Gao<br />

(2002), who found fi ve-fold variation in IC 50 (concentration producing 50% inhibition of<br />

larval development of third-instars). The IC 50 ranged from 0.020 to 0.105 μg 1 mL, 0.016 to<br />

0.099 μg 1 mL, and 0.016 to 0.080 μg 1 mL for 1998, 1999, and 2000 insect populations,<br />

respectively.<br />

Holloway and Dang (2000) did not observe any differences in susceptibility of H. armigera<br />

and Helicoverpa punctigera (Wallengren) in cotton, in contrast to sweetcorn, using a discriminating<br />

concentration (10.02%) of MVP II formulation of Cry1Ac in Australia. Helicoverpa<br />

armigera is more tolerant to Bt toxins than H. punctigera (Liao, Heckel, and Akhurst, 2002).<br />

Only Cry1Ab, Cry1Ac, Cry2Aa, Cry2Ab, and Vip 3 killed H. armigera at dosages that could<br />

be considered to be effective for controlling this pest. There were no differences in the<br />

relative toxicity of Cry1Fa and Cry1Ac for H. punctigera, but Cry1Fa showed little toxicity to<br />

H. armigera. The differences in susceptibility to Cry1Ac and Cry2Aa were signifi cant.<br />

The LC 50 of Cry1Ac to Earias vittella (F.) ranges from 0.006 to 0.105 μg g 1 of diet, representing<br />

a 17.5-fold variation in susceptibility from 27 locations in India (Kranthi et al.,<br />

2004). Variation in a majority of sites was around 10%. The strains collected from South<br />

India showed greater variation in susceptibility to Bt toxins. Reed and Halliday (2001)<br />

established Cry9C baseline susceptibility for fi eld-collected populations of European<br />

corn borer, O. nubilalis and Southwestern corn borer, Diatraea grandiosella (Dyar). For the<br />

European corn borer, LC 50 values ranged from 13.2 to 65.1 ng cm 2 , and the LC 90 values<br />

from 46.5 to 214 ng cm 2 . The LC 50 values for neonate larvae of Southwestern corn borer

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