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

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of alkylphenol polyethoxylates in carbaryl- or carbofuran- containing formulations. Adjuvants<br />

are frequently mixed with formulations prior to applications, so although they may not be present<br />

in the formulations they could still be co-applied. Below we discuss NP’s toxicity as an example<br />

of potential adjuvant toxicity, as we received no information on adjuvant use or toxicity within<br />

the BEs.<br />

We queried EPA’s ECOTOX online database <strong>and</strong> retrieved 707 records of nonylphenol’s (NP)<br />

acute toxicity to freshwater <strong>and</strong> saltwater species. The lowest reported LC50 for a salmonid was<br />

130 μg/L for Atlantic salmon. Aquatic invertebrates, particularly crustaceans, were killed at low<br />

concentrations of NP, with the lowest reported LC50 = 1 μg/L for H. azteca. These data indicate<br />

that a wide array of aquatic species are killed by NP at μg/L concentrations. We also queried<br />

EPA’s ECOTOX database for sublethal toxicity <strong>and</strong> retrieved 689 records of freshwater <strong>and</strong><br />

saltwater species tested in chronic experiments. The lowest fish LOEC reported was 0.15 μg/L<br />

for fathead minnow reproduction. Numerous fish studies reported LOECs at or below 10 μg/L.<br />

Additionally, salmonid prey species are sensitive to sublethal effects of NP at low μg/L<br />

concentrations. The amphipod, Corophium volutator, grew less <strong>and</strong> had disrupted sexual<br />

differentiation (Brown, Conradi et al. 1999). Multiple studies with fish indicated that NP<br />

disrupts fish endocrine systems by mimicking the female hormone 17β-estradiol (Brown <strong>and</strong><br />

Fairchild 2003; Arsenault, Fairchild et al. 2004; Madsen, Skovbolling et al. 2004; Jardine,<br />

MacLatchy et al. 2005; Luo, Ban et al. 2005; McCormick, O'Dea et al. 2005; Segner 2005;<br />

Hutchinson, Ankley et al. 2006; Lerner, Bjornsson et al. 2007; Lerner, Bjornsson et al. 2007).<br />

NP induced the production of vitellogenin in fish at concentrations ranging from 5-100 μg/L<br />

(Hemmer, Bowman et al. 2002; Ishibashi, Hirano et al. 2006; Arukwe <strong>and</strong> Roe 2008;<br />

Schoenfuss, Bartell et al. 2008). Vitellogenin is an egg yolk protein produced by mature females<br />

in response to 17-β estradiol, however immature male fish have the capacity to produce<br />

vitellogenin if exposed to estrogenic compounds. As such, vitellogenin is a robust biomarker of<br />

exposure. A retrospective analysis of an Atlantic salmon population crash suggested the crash<br />

was due to NP applied as an adjuvant in a series of pesticide applications in Canada (Fairchild,<br />

Swansburg et al. 1999; Brown <strong>and</strong> Fairchild 2003). Additionally, processes involved in sea<br />

water adaptation of salmonid smolts are impaired by NP (Madsen, Skovbolling et al. 2004;<br />

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