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HERBICIDES in Asian rice - IRRI books - International Rice ...

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Table 1. Number of papers deal<strong>in</strong>g with the impact of herbicides a on microorganisms<br />

<strong>in</strong> California <strong>rice</strong>fields, 1990.<br />

Herbicide<br />

Algae and<br />

cyanobacteria<br />

Bacteria<br />

Lab b Pot Field Lab Pot Field<br />

Bensulfuron methyl<br />

Copper sulfate<br />

2,4-D<br />

Glyphosate<br />

MCPA<br />

Mollnate<br />

Pendimethal<strong>in</strong><br />

Propanil<br />

Thiobencarb<br />

Total<br />

2 6<br />

21 2 1<br />

2<br />

5 1 1<br />

3 1 1 1 1<br />

7 1 3 2<br />

5 1 1 1<br />

45 2 14 5 20<br />

a Listed by Crosby (1996).<br />

b Lab = laboratory.<br />

— Most studies are laboratory experiments with cultures of microorganisms<br />

or with only a few grams of soil. Less than 8% of the quantitative studies<br />

were conducted <strong>in</strong> <strong>rice</strong>fields. Experiments with microbial cultures give an<br />

<strong>in</strong>dex of a stra<strong>in</strong>'s sensitivity to pesticides, but the results cannot be extrapolated<br />

to field conditions where the <strong>in</strong>itial concentrations of pesticides<br />

are likely to decrease rapidly, as their degradation is hastened by soil microflora,<br />

nonbiological decomposition, leach<strong>in</strong>g, volatilization, and soil<br />

adsorption. Concentrations of pesticides that affect microorganism growth<br />

depend on the <strong>in</strong>itial microbial population, its nutrient status, the method<br />

of pesticide application, and the degradation products. These factors markedly<br />

differ <strong>in</strong> vitro and <strong>in</strong> situ. For example, little agreement was found<br />

between the responses of microbial species to glyphosate <strong>in</strong> <strong>in</strong>cubated soil<br />

samples and <strong>in</strong> pure culture (Wardle and Park<strong>in</strong>son 1990).<br />

— Many studies used pesticide concentrations higher than those result<strong>in</strong>g<br />

from the recommended level for field application. Such experiments may<br />

overestimate pesticide persistence because degradation is slowed at high<br />

concentrations, as has been shown with triflural<strong>in</strong> (Parr and Smith 1973)<br />

and mol<strong>in</strong>ate (Deul et al 1978). The recommended levels of traditional<br />

pesticides range from a few hundred grams to a few kilograms of active<br />

<strong>in</strong>gredient per hectare. The median recommendation for herbicides (2.5<br />

kg ai ha -1 ) is higher than it is for fungicides (1.7 kg ai ha -1 ) and <strong>in</strong>secticides<br />

(1.1 kg ai ha -1 ) (Roger 1990). Experimental results should be <strong>in</strong>terpreted<br />

<strong>in</strong> the context of the range of pesticide concentrations that can be expected<br />

<strong>in</strong> farmers' fields after application. If a herbicide applied on a nonflooded<br />

field stays with<strong>in</strong> the surface 2 cm of soil, 2.5 kg ai ha -1 would correspond<br />

to 15 mg kg -1 dry weight of soil, for a bulk density of 1 mg m -3 . If a water-<br />

Effect of herbicide use on soil microbiology 71

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