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a four-fold rise - Center for Food Safety

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<strong>Center</strong> <strong>for</strong> <strong>Food</strong> <strong>Safety</strong> – Science Comments – FG72 Soybean <br />

15 <br />

the pattern of application will differ. If FG72 soybean is adopted <strong>for</strong> use on the same number <br />

of acres as isoxaflutole is used on corn – 7% -­‐ then use of isoxaflutole at the landscape level <br />

will double. (We estimate that adoption of FG72 soybean will be much higher than that, and <br />

that use on corn will also increase, so that 4 times more isoxaflutole is possible, as we have <br />

discussed.) The point here is that even if the amount of isoxaflutole is the same with FG72 <br />

soybean as it now is in corn – same number of acres, same application rate, same number of <br />

applications – twice the amount isoxaflutole will be used in regions where both are grown. <br />

This landscape-­‐level increase in isoxaflutole use is likely to have impacts on water quality. <br />

Within a watershed draining corn and soybean fields there will be twice the load of <br />

isoxaflutole entering the system. Basically, the number of agricultural non-­‐point sources <strong>for</strong> <br />

isoxaflutole pollution will increase (DEA at 12). We discuss all of these impacts later in thesthe <br />

comments: isoxaflutole, and particularly its degradates, enter surface water through runoff <br />

and leaching <strong>for</strong> quite a while after it is are applied, and can persist and accumulate in water at <br />

levels that are harmful to non-­‐target organisms, including threatened and endangered species. <br />

Biodiversity may thus be diminished. These increased loads may also affect drinking water, <br />

and human health. The propensity of isoxaflutole applications to contaminate water with risk <br />

of harm to non-­‐target plants is the reason <strong>for</strong> its restricted use status (DEA at 35, 93 – 95). A <br />

greater portion of the landscape sprayed with isoxaflutole may also accelerate weed <br />

resistance. APHIS must assess the cumulative impacts from isoxaflutole use on corn and FG72 <br />

soybean in the same landscape. <br />

ii. Isoxaflutole appliations in sequence <br />

Corn – FG72 soybean rotations on the same acreage with isoxaflutole applied in succession <br />

also may have cumulative impacts, as we discuss below: isoxaflutole has residual activity in <br />

soil, killing germinating seedlings after rains <strong>for</strong> weeks; and requiring waiting periods of <br />

months to a year and a half, accompanied by specified amounts of rainfall, be<strong>for</strong>e other crops <br />

can be planted. Drought results in increased soil retention of isoxaflutole residues and its <br />

degradates, possibly increasing the waiting times, too. Under some conditions, isoxaflutole <br />

may be applied in the second year on top of residual isoxaflutole from the year be<strong>for</strong>e, perhaps <br />

leading to higher contamination of water, or to unexpected injury in other rotation crops. Non-­target<br />

wild plant populations, including threatened and endangered species, that are <br />

particularly sensitive to isoxaflutole may be more adversely affected by use of isoxaflutole in <br />

successive years than from intermittent applications. Biodiversity may thus be diminished. <br />

Also, use of herbicides with the same mode of action on the same acreage in successive years is <br />

a risk factor <strong>for</strong> promotion of resistant weeds, including isoxaflutole resistance and resistance <br />

to multiple herbicides. APHIS needs to consider the cumulative impacts of rotating corn with <br />

FG72 soybean.

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