Consultant's Report - Minnesota State Legislature
Consultant's Report - Minnesota State Legislature
Consultant's Report - Minnesota State Legislature
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Pre-fertilization andpost-fertilization tests<br />
These tests were designed to address effects of Cu treatments on fertilization rate.<br />
In the pre-fertilization tests, addition of Cu solutions to eggs prior to fertilization<br />
addressed treatment effects on gamete viability, fertilization processes and 0 to 24-h<br />
development of larvae. In contrast, the post-fertilization tests enabled measurement of<br />
treatment effects during 0 to 24-h development. Significant differences in sensitivity<br />
between the pre-fertilization and post-fertilization tests were interpreted as treatment<br />
effects upon gamete viability and fertilization processes. For post-fertilization tests, Cu<br />
solutions were added 2: 15 min after sperm addition, to allow fertilization in the absence<br />
of Cu treatments. Effects of Cu solutions on fertilization rate were assessed by recording<br />
the number of living larvae as a fraction of eggs added per well. Moving larvae were<br />
considered to be alive.<br />
Pre-veliger tests<br />
These tests addressed the effects of Cu treatments on 24-h-, 48-h- and 72-h-old<br />
larvae. At the start of each test, the number of living pre-veligers was recorded and the<br />
appropriate Cu spiking solution was added. At test termination, surviving larvae were<br />
counted.<br />
Data analyses<br />
Data were analyzed using trimmed Spearman-Karber probit analysis to estimate<br />
LCso and LC99 values and, when the model allowed, 95 % confidel}ce limits. Control<br />
mortality was corrected using Abbott's correction. TRVs were considered significantly<br />
different when 95 % confidence limits did not overlap. ToxCalc© software was used for<br />
all analyses (Tidepool Scientific, McKinleyville, CA).<br />
Results and Discussion<br />
Results for LCso data are summarized in Table 2. LCso 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 />
Results from experiment 1 reveal that LCso data for Cutrine®-Ultra were similar in<br />
all stages of larval development from post-fertilization to 72 h old, ranging from 0.008 to<br />
0.013 mg CulL. These values were also similar to those for Cu as CUS04, which ranged<br />
from 0.007 - 0.008 mg CulL. These findings suggest that, for these life stages, Cu is the<br />
active toxic compound in Cutrine®-Ultra, and that Cutrine®-Ultra toxicity might be<br />
predicted by Cu concentration alone. In contrast, Cutrine®-Ultra exhibited a significantly<br />
higher toxicity in the pre-fertilized egg exposures than did Cu alone. This was confirmed<br />
by the third experiment, which utilized lower exposure concentrations to enable a more<br />
definitive estimate of LCso. Comparison of these data with those for Cu also indicates<br />
that the toxicity of Cutrine®-Ultra to pre-fertilization stage eggs was higher than that<br />
associated with Cu alone.<br />
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