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

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100<br />

80<br />

n<br />

itio<br />

h<br />

ib<br />

60<br />

in<br />

E<br />

h<br />

C<br />

A<br />

40<br />

%<br />

20<br />

A. B.<br />

Mixture<br />

M 8 5 ug/L<br />

Cn 19 ug/L<br />

Cl 41 ug/L<br />

0<br />

0.0 01 0.01 0 .1 1 10 1 00 1000<br />

Concentration relative to E C50<br />

10 0<br />

80<br />

lity<br />

60<br />

r<br />

ta<br />

o<br />

m<br />

% 40<br />

386<br />

20 Cl 41 ug/L<br />

Cn19 ug/L<br />

M 85 ug/L<br />

Mixture<br />

0<br />

0.0 01 0.01 0 .1 1 10 1 00 100 0<br />

Concentration relative to LC50<br />

Figure 42. Percent AChE inhibition (A.) <strong>and</strong> percent mortality (B.) for salmonids expected from<br />

exposure to carbaryl (Cl), carbofuran (Cn), <strong>and</strong> methomyl (M) as separate constituents <strong>and</strong> as<br />

mixtures (Cl 41 µg/L, Cn 19 µg/L, <strong>and</strong> M 85 µg/L) 4 .<br />

We used a variety of exposure estimates <strong>and</strong> monitoring data to evaluate responses to different<br />

mixtures of carbaryl, carbofuran, <strong>and</strong> methomyl (Table 73). The predicted additive responses<br />

from these mixtures ranged from 16-74% inhibition of AChE <strong>and</strong> 0.01-74% mortality. The<br />

predicted additive response to AChE inhibition is likely to result in increased behavioral<br />

consequences to salmonids. What is not captured in these responses is the likelihood of exposure<br />

to the various mixture concentrations. The PRZM-EXAMS values were estimates selected from<br />

EPA simulations of western crops. The scenarios were representative of use rates <strong>and</strong> numbers<br />

of applications on current product labels. Additionally, we used 60 d, time-weighted averages of<br />

exposure rather than predicted peak concentrations as exposure to multiple pesticides would be<br />

expected to occur more frequently over chronic durations. This may underestimate effects as<br />

responses assumed 96 h exposure. Site specific considerations will also have an influence on the<br />

frequency of exposure.<br />

4 EPA's default pesticide slope was used for acute mortality (3.63 or probit slope of 4.5) [EPA 2004]. The slope<br />

used for AChE inhibition was based on pooling data from five cholinesterase-inhibiting insecticides; including<br />

carbofuran, carbaryl, chlorpyrifos, diazinon, <strong>and</strong> malathion Laetz, C. A., D. H. Baldwin, et al. (2009). "The<br />

synergistic toxicity of pesticide mixtures: Implications for risk assessment <strong>and</strong> the conservation of endangered<br />

Pacific salmon." Environmental Health Perspectives 117: 348-353..

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