Consultant's Report - Minnesota State Legislature
Consultant's Report - Minnesota State Legislature
Consultant's Report - Minnesota State Legislature
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Table 2. Summary ofLCso values.<br />
Expt Chemical<br />
Pre-fert<br />
LCso<br />
Post-fert<br />
LCso<br />
24-h<br />
LCso<br />
48-h<br />
LCso<br />
72-h<br />
LCso<br />
1<br />
Cutrine 0.001<br />
0.013<br />
(0.006 0.019)<br />
0.008<br />
(0.002 - 0.014)<br />
0.009 0.012<br />
CUS04 - - 0.008 - 0.007<br />
2<br />
3'<br />
Cutrine - - - - -<br />
CUS04<br />
0.004<br />
(0.002 - 0.005)<br />
0.005 - - -<br />
Cutrine 0.002 - - - -<br />
CUS04 - - - - -<br />
Since there was no difference in the toxicity of Cutrine®-Ultra and Cu to postfertilization<br />
stage eggs, we conclude that Cutrine®-Ultra has a mode of toxicity upon<br />
gamete viability or the fertilization physiology other than that associated with Cu<br />
exposure.<br />
Literature TRVs for D. polymorpha are scarce, although Fisher et al. (1994)<br />
determined LCso values for six molluscides and concluded that larvae were more<br />
sensitive than adults to five of the compounds. The only Cu-related D. polymorpha<br />
information that these authors are aware ofis unpublished by McMahon and Tsou (1990)<br />
from a conference proceeding, indicating that 5 mg CulL 100 % mortality of D.<br />
polymOlpha veliger in 24 h in unknown water quality conditions. Based on results from<br />
the current study, such levels of mortality can be achieved at much lower concentrations<br />
ofCu in Lake Ossawinnamakee water.<br />
Results for LC99 data are summarized in Table 3. LC99 values are shown in bold<br />
type, and 95 % confidence limits in parentheses where the model allowed this estimation.<br />
All data are mg CulL.<br />
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