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Impact of - IDL-BNC @ IDRC - International Development Research ...

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Progress in improving safety<br />

Pesticides in use at the turn <strong>of</strong> the century typically had a broad spectrum <strong>of</strong><br />

biological activity and a low level <strong>of</strong> pesticidal activity. They were not particularly<br />

toxic to humans, but had to be applied in large quantities (compared<br />

with current application rates) to compensate for their low potency. The<br />

resulting human health hazard could, therefore, become significant.<br />

<strong>Research</strong> has focused primarily on improving selectivity, i.e., enhancing the<br />

pesticidal activity on target species while leaving nontarget species, including<br />

man, more or less untouched. In the process, a higher efficacy is usually also<br />

obtained.<br />

Qualitative selectivity is achieved when a pesticide interferes with a process<br />

or processes that occur only in the target species. For example, inhibition (by<br />

an acylurea pesticide) <strong>of</strong> chitin formation, which is essential for the formation<br />

<strong>of</strong> the legs, shield, etc., <strong>of</strong> insects, does not affect mammals. Interfering with<br />

photosynthesis in weeds does not harm birds and mammals as these organisms<br />

do not photosynthesize. Herbicides may, therefore, have a favourable<br />

toxicity pr<strong>of</strong>ile (Table 2).<br />

Quantitative selectivity, on the other hand, is based on differences between<br />

the target and nontarget species that determine susceptibility, e.g., skinpenetration<br />

rate, metabolism (toxification or detoxification), and excretion<br />

rate. A drawback <strong>of</strong> quantitative selectivity is the possibility that the target<br />

species becomes resistant. The properties that make nontarget species less<br />

susceptible to the pesticide may, in a number <strong>of</strong> generations, be acquired by<br />

the target species through genetic selection. Oppenoorth and Besemer<br />

Table 2. Comparative toxicity <strong>of</strong> several herbicides, aspirin,<br />

and caffeine.<br />

Product<br />

LD5o in rats<br />

(mg/kg)<br />

Caffeine 200<br />

Alachlor 1 200<br />

Cyanazine 1 200<br />

Aspirin 1 750<br />

Metribu2in 2 200<br />

Terbutryme 2 380<br />

Flamprop-isopropyl >3000<br />

Glyphosate 4 320<br />

Terbacil 5 000<br />

Asulam > 5 000<br />

Imazapyr > 5 000<br />

Sulfometuron-methyl > 5 000<br />

Chlortoluron<br />

Source: Graham-Bryce (1990).<br />

> 10 000<br />

147

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