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

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Sample sites for this study are best characterized as integration sites selected based on the<br />

presence of the listed Yakima salmonid population (one of 17 independent populations that<br />

comprise the Middle Columbia River steelhead DPS) <strong>and</strong> high diversity <strong>and</strong> intensity of<br />

agriculture. The study design included sampling during the pesticide application season but did<br />

not target specific applications of pesticides nor did it target salmonid habitats that would be<br />

expected to produce the highest concentrations of pesticides (e.g., shallow off-channel habitat in<br />

close proximity to pesticide application sites). Sampling was generally conducted on a weekly<br />

basis, so it is likely peak concentrations associated with drift <strong>and</strong> runoff events were not<br />

captured. Sampling stations included both agricultural- <strong>and</strong> urban-dominated watersheds, <strong>and</strong><br />

some storm events are captured in the sampling. Sampling favored the detection of multiple<br />

pesticides, rather than peak concentrations in some habitats used by Middle Columbia River<br />

steelhead.<br />

Other available monitoring data are also applicable to assessing exposure in listed salmon, but to<br />

varying degrees. Common aspects that limit the utility of the available monitoring data as<br />

accurate depictions of exposure within listed salmonid habitats include: 1) protocols were not<br />

designed to capture peak concentrations or durations of exposure in habitats occupied by listed<br />

species; 2) limited utility as a surrogate for other non-sampled surface waters; 3) lack of<br />

representativeness of current <strong>and</strong> future pesticide uses <strong>and</strong> conditions; <strong>and</strong> 4) lack of information<br />

on actual pesticide use to correlate with observed surface water concentrations.<br />

Protocols not designed to capture peak exposure. The NAWQA monitoring studies contain the<br />

largest data set evaluated. However, these studies were designed to evaluate trends in water<br />

quality <strong>and</strong> were not designed to characterize exposure of pesticides to listed salmonids (Hirsch<br />

1988). The NAWQA design does not result in an unbiased representation of surface waters. For<br />

example, some agricultural activities <strong>and</strong> related pesticide uses that may be very important in a<br />

particular region may not be represented in the locations sampled. Sampling from the NAWQA<br />

studies <strong>and</strong> other studies reviewed was typically not conducted in coordination with specific<br />

applications of carbaryl, carbofuran, <strong>and</strong> methomyl. Similarly, sampling was not designed with<br />

consideration to salmon distribution or to target the salmonid habitats most likely to contain the<br />

greatest concentrations of pesticides. Given the relatively rapid dissipation of these pesticides in<br />

302

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