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Carbaryl, Carbofuran, and Methomyl - National Marine Fisheries ...

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Application Rate Water Depth A.i. Concentration in Surface<br />

Water<br />

(lbs a.i. / acre) (meters) (μg/L)<br />

0.25 0.1 280<br />

0.5 0.1 560<br />

1 0.1 1121<br />

3 0.1 3363<br />

10 0.1 11208<br />

Pesticide drift<br />

We also provide estimated pesticide concentrations in shallow off-channel habitats associated<br />

with drift from terrestrial applications of pesticides (Table 52). These estimates were derived<br />

using the AgDrift model <strong>and</strong> estimate downwind deposition from pesticide drift (Teske 2001).<br />

Additional deposition from runoff was not considered. The drift estimates derived represent<br />

mean projected drift. Although AgDrift adequately predicts drift, its field validations studies <strong>and</strong><br />

other research show drift is highly variable <strong>and</strong> influenced by site-specific conditions <strong>and</strong><br />

application equipment (Bird, Perry et al. 2002). No-spray buffer zones (or setbacks) may<br />

significantly reduce pesticide exposure to salmonids by reducing runoff <strong>and</strong> drift inputs.<br />

The methomyl RED requires label statements for methomyl products that specify not to “apply<br />

by ground equipment within 25 ft, or by air within 100 ft of lakes, reservoirs, rivers, estuaries,<br />

commercial fish ponds <strong>and</strong> natural, permanent streams, marshes or natural, permanent ponds.<br />

Increase the buffer zone to 450 ft from the above aquatic areas when ultra low volume<br />

application is made (EPA 1998).” This label requirement appears to address many, but not all<br />

aquatic habitats used by listed salmonids. For example, labels specify buffers to natural <strong>and</strong><br />

permanent streams, marshes, <strong>and</strong> ponds but there is no mention of important intermittent aquatic<br />

habitats or manmade watercourses such as floodplain restoration sites <strong>and</strong> irrigation systems that<br />

either contain listed species or drain to such habitats.<br />

Specific buffer zones that correspond to current label requirements for carbaryl, carbofuran, <strong>and</strong><br />

methomyl were assessed (Table 52). No buffers to aquatic habitats are required by EPA for<br />

carbaryl or carbofuran products. However, we did consider interim “voluntary” buffers<br />

recommended by CDPR to protect federally listed endangered species<br />

(http://www.cdpr.ca.gov/docs/endspec/prescint.htm). Our simulations assumed the off-channel<br />

288

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