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

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(Detra <strong>and</strong> Collins 1986; Detra <strong>and</strong> Collins 1991) <strong>and</strong> vertebrates including salmonids following<br />

exposures to carbamates <strong>and</strong> OPs (Beyers <strong>and</strong> Sikoski 1994, Eder et al. 2007, Grange 2002, Hoy<br />

et al. 1991, Laetz et al. 2009, Li H. X. et al. 2008, Li S. N. <strong>and</strong> Fan 1996, Liu et al. 2007,<br />

S<strong>and</strong>ahl J. F. et al. 2004, S<strong>and</strong>ahl J.F. et al. 2005, Scholz et al. 2006, St. Aubin 2004, Tierney et<br />

al. 2007, Yi et al. 2006, Zinkl et al. 1987).<br />

One highly relevant study measured inhibition of brain AChE, duration of recovery, survival at<br />

24 h, <strong>and</strong> tissue concentrations in juvenile rainbow trout (O. mykiss) following exposure to<br />

carbaryl at 0, 250, 500, 1,000, 2,000, <strong>and</strong> 4,000 μg/L (Zinkl, Shea et al. 1987). Rainbow trout<br />

showed dose-dependent AChE inhibition from 61 to 91 % when exposed to 250 – 4,000 μg/L for<br />

24 h. Most trout that died had 85% or greater inhibition. Trout recovered AChE activity<br />

following 24 h in uncontaminated water, indicating that fish recover if given the opportunity<br />

following carbamate exposures (Zinkl, Shea et al. 1987). This study showed that carbaryl is<br />

acutely toxic to rainbow trout in a matter of hours (incidences of death at 1.5 – 4 h) at<br />

concentrations at or above 1,000 μg/L.<br />

pH <strong>and</strong> toxicity<br />

We located several data sets on toxicity to freshwater fish <strong>and</strong> aquatic invertebrates exposed to<br />

carbaryl <strong>and</strong> carbofuran at different pHs (Mayer <strong>and</strong> Ellersieck 1986). Acute toxicity of carbaryl<br />

<strong>and</strong> carbofuran increases as pH increased, based on the available freshwater fish assays (Mayer<br />

<strong>and</strong> Ellersieck 1986). This largely is considered a result of the influence pH has on the creation<br />

of hydrolysis products (Mayer <strong>and</strong> Ellersieck 1986). However, the persistence of carbaryl <strong>and</strong><br />

carbofuran is reduced as pH increases. As noted in the exposure section, degradation half-lives<br />

can vary from hours (in alkaline waters) to weeks (in acidic waters) depending on pH. Within<br />

the Pacific Northwest <strong>and</strong> California pH varies seasonally <strong>and</strong> typically may range from 6 – 9.<br />

For methomyl, pH seems to have less of an influence on hydrolysis rates. Due to the influence<br />

of pH on persistence of carbaryl <strong>and</strong> carbofuran, we evaluated reported toxic effects within the<br />

context of pH if provided <strong>and</strong> discuss pH in relationship to salmonid habitat utilization.<br />

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