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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information that these authors are aware ofis unpublished by McMahon and Tsou (1990)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 />

15

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