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

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Acute EC50s are also reported for several species of estuarine/marine shrimp in both the BE<br />

(EPA 2003) <strong>and</strong> the RED Science Chapter (EPA 1998). Again, there are inconsistencies<br />

between the documents, with the same EC50s from formulation tests reported in the BE as 30%<br />

a.i. <strong>and</strong> in the Science Chapter as 24% a.i. Some EC50s were also reported for the a.i. Only one<br />

species, grass shrimp (Palmonetes vulgaris) appears to have been tested with both the a.i. <strong>and</strong> the<br />

formulation (EPA 2003). In this case, the formulation (EC50 130 μg/L, reported as a 30% a.i.),<br />

appears less toxic than the technical (EC50 49 μg/L). Other EC50s listed in the BE were for<br />

pink shrimp (P. duorarum, 19 μg/L) <strong>and</strong> mysid shrimp (M. bahia, 230 μg/L), both of which<br />

appear to be technical a.i. (90-98.4%).<br />

The methomyl BE (EPA 2003) reports NOAECs <strong>and</strong> LOAECs for reproductive endpoints for<br />

two studies conducted on D. magna, both with the technical a.i. In one study, with a NOAEC of<br />

0.4 μg/L <strong>and</strong> a LOAEC of 0.8 μg/L, the number of young per female was reduced. A second<br />

resulted in a NOAEC of 1.6 μg/L <strong>and</strong> a LOAEC of 3.1 μg/L, based on an unspecified<br />

reproductive endpoint. The BE also reports a NOAEC of 29 μg/L <strong>and</strong> a LOAEC of 59 μg/L for<br />

the estuarine mysid shrimp, based on “reproduction <strong>and</strong>/or growth.”<br />

The BE <strong>and</strong> Science Chapter both report on an outdoor microcosom study conducted with<br />

methomyl (MRID 437444-02). The Science Chapter, Appendix C (EPA 1998), describes the<br />

study design as: “<strong>Methomyl</strong> was applied to seven treatment groups, at two application rates, at<br />

three different application intervals, over a period of 22 days (pg 51).” Specific application rates<br />

<strong>and</strong> intervals were not provided, nor was use of a control specifically mentioned. Zooplankton<br />

(Cladocera, Copepodia <strong>and</strong> Rotifera) abundance <strong>and</strong> community composition were altered in at<br />

least some treatments, <strong>and</strong> Ephemeroptera abundance decreased in the two highest treatments.<br />

Toxicity of <strong>Carbaryl</strong>, <strong>Carbofuran</strong>, <strong>and</strong> <strong>Methomyl</strong> Degradates<br />

The BEs briefly addressed the issues of degradates. The carbaryl BE (EPA 2003c) provides<br />

acute fish <strong>and</strong> invertebrate toxicity data the degradate, 1-napthol. The LC50s for three species of<br />

fish tested (freshwater (O. mykiss, Lepomis macrochirus)) <strong>and</strong> marine/estuarine (Cyprinodon<br />

varigatus) range from 750 – 1,800 μg/L. LC50s presented for aquatic invertebrates include 700-<br />

330

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