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Hope Not Hype - Third World Network

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Pesticides<br />

71<br />

(Box 6.1 continued)<br />

The claim of an indirect benefit through lower costs or higher profits is also<br />

questionable. It would appear that any benefit of insecticidal crops for reducing<br />

mycotoxins is to reduce the cost of using high-rent GM seeds and chemically intensive<br />

farming practices. Integrated pest management and agroecological methods are far more<br />

promising and sustainable strategies for controlling insect damage to crops (Chapter 7).<br />

The benefit of insecticidal plants would be to reduce the high cost of using GM seeds<br />

and proprietary insecticides rather than a net benefit to the food supply. This benefit<br />

claim requires more systematic study including using the best alternative agricultural<br />

models (see Chapter 7) as controls (Benbrook, 2005).<br />

Felicia Wu, in a paper on the economic benefits of Bt plants, found that there<br />

could be a maximum economic benefit to the US of US$23 million/year (Wu, 2006).<br />

But even the economic benefit needs to be kept in perspective. Recall that the US corn<br />

farmer is heavily subsidized. According to a report of the Congressional Research Service,<br />

corn subsidies in the US averaged US$4.5 billion per year, with a peak of US$10.1<br />

billion in 2000 (Schnepf and Womach, 2007). At US$23 million/year, the net reduction<br />

in the costs of mycotoxin would amount to a scant 0.5% of the public loss on corn in<br />

general. Sadly, the maximum possible economic benefit of insecticidal plants would<br />

not even recover the amount that the corn biofuel lobby paid to US politicians on average<br />

per year over a recent 15-year period (Schubert, 2006).<br />

specific (Delmer, 2005) (Box 6.1). The reporting of benefits and harms has been heavily<br />

generalized, which has the effect of reducing the accuracy of reporting. Furthermore, there<br />

are clear gaps in some aspects of safety testing, including human health and non-target<br />

effects. The main point for the Assessment was that it was not possible to extrapolate to a<br />

definitive endorsement of genetic engineering from the existing context-dependent data.<br />

Human health and environmental risks from herbicide-tolerant crops<br />

Like with other herbicides, there is a price to pay for using commercial formulations<br />

of glyphosate and glufosinate even though they are claimed to be less toxic to humans and<br />

less harmful to the environment.<br />

Environmental benefits centre around the use of more benign herbicides than many of the<br />

alternative products that may be used in the equivalent non-HT crop, fewer herbicide<br />

applications, and reduced tillage, since herbicide incorporation into the soil is not necessary<br />

(Devine, 2005, p. 313).<br />

Herbicide formulations can also have non-target effects. Glyphosate formulations<br />

can be toxic to some animals (e.g., see Relyea, 2005; Relyea et al., 2005, but also challenged<br />

by Thompson et al., 2005) or tissues (Benachour and Séralini, 2009; Richard et al., 2005).<br />

Although glyphosate is claimed to have a lower toxicity to humans than many other<br />

alternative herbicides (Alan, 2000), these claims may be oversimplifications of the true<br />

impact of glyphosate-based commercial formulations which rely on a number of other

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