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laboratory (Wardle, 1972). In the last two samples, February 1980<br />

and June 1980, reference plaice were sampled very rapidly a^ter capture<br />

and their blood glucose values represent the normal unstressed values.<br />

Plaice from the Abers were stressed by capture and showed a hyperglycemic<br />

response, suggesting some recovery of physiological function<br />

with time. These data show some of the difficulties in using blood<br />

glucose concentration as an index of stress in fish. If blood samples<br />

cannot be taken immediately after the fish are captured, capture- induced<br />

responses may obscure any due to pollution.<br />

Liver glycogen concentrations in fish from the last two collections<br />

were highly variable (Table 21). Because of extremely large standard<br />

deviations, no patterns could be discerned.<br />

Total cholesterol and high density lipoprotein (HDL) cholesterol<br />

concentrations in the blood of plaice were measured in sampels from the<br />

last two collecting trips (Table 22). The general trend was for total<br />

cholesterol to be elevated and HDL cholesterol concentration to be<br />

depressed in fish from the two oil-contaminated Abers. Several of these<br />

differences were statistically significant. As a result, HDL cholesterol<br />

as percent of total cholesterol was lower in plaice from Aber Benoit and<br />

Aber Wrac'h than in plaice from the reference station at lie Tudy.<br />

Concentration of liver-free ascorbic acid was measured in plaice<br />

from all five sampling trips (Table 23). In all but the February 1980<br />

sample, liver ascorbate concentrations in plaice from oil-contaminated<br />

Aber Benoit and Aber Wrac'h were substantially lower than concentrations<br />

in livers of plaice from reference stations. In four cases, the difference<br />

was statistically significant. In the February collection, the<br />

pattern was reversed. Reference fish contained hepatic ascorbate concentrations<br />

significantly lower than concentrations in livers of fish from<br />

the two Abers. At this time, all the reference fish were gravid females<br />

ready to spawn. Only a few of the fish from the Abers were in this condition.<br />

It is highly likely that the extreme depletion of liver ascorbate<br />

reserves in the reference fish is the result of ascorbate mobilization<br />

for gonadal maturation and ovogenesis. These gravid reference fish also<br />

had relatively low hepatic glycogen reserves (Table 21) .<br />

Adductor muscle-free amino acid profiles and concentrations were<br />

measured in oysters from the first three collecting trips<br />

Total free amino acid concentrations were always lower in<br />

(Tables 24-26).<br />

adductor muscles<br />

of oysters from oil-contaminated Aber Benoit and Aber Wrac'h than in<br />

adductors of oysters from reference stations. This difference cannot<br />

be attributed to differences in seawater salinity between Aber and<br />

reference stations, since all stations had salinities in the 30-34 o/oo<br />

307

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