Proceedings - Teaching and Learning Centre - Simon Fraser ...
Proceedings - Teaching and Learning Centre - Simon Fraser ...
Proceedings - Teaching and Learning Centre - Simon Fraser ...
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<strong>Fraser</strong> River Action Plan 3rd Research Workshop<br />
techniques were all used to improve the capture success of mature peamouth chub. The greatest numbers of<br />
peamouth were caught in eddy pools along the margins of the river using sinking, monofilament gillnets (50 mm<br />
mesh). Despite substantial sampling effort, numbers of mature male/female fish captured in the exposure zones<br />
were again limited. Capture success was strongly hindered by high, turbid water levels <strong>and</strong> large amounts of<br />
suspended debris which fouled the gillnets.<br />
Conclusions<br />
Overall, there were few differences in whole organism <strong>and</strong> physiological parameters between fish collected from<br />
the reference <strong>and</strong> near-field zones. Limited sample sizes for mature male <strong>and</strong> female fish made it difficult to<br />
confidently compare characteristics between zones. However, a graphical approach comparing the spatial<br />
position of individual near-field fish relative to the 95% confidence ellipse of reference fish did not show<br />
substantial deviations in the parameters of exposed chub. As in the fall survey, immature peamouth chub from<br />
the near-field zones had induced EROD activity (1.5- to 4.1-fold) relative to reference fish, indicating exposure<br />
to mill effluent. No steroid hormone differences (circulating levels or in vitro production) were observed<br />
between reference <strong>and</strong> exposed fish. Comparisons between spring <strong>and</strong> fall reference fish indicated that sexually<br />
mature fish collected in the spring were significantly larger <strong>and</strong> older than fish collected during the fall survey.<br />
These results further supported the hypothesis that chub collected during the fall were probably borderline in<br />
terms of size <strong>and</strong> age of maturity.<br />
As in the fall, instream concentrations of conductivity, chloride, sodium <strong>and</strong> suphate were predictably higher<br />
downstream of the mill diffusers during the spring survey. Chloride data indicated that effluent concentrations<br />
were approximately 0.08-0.6% downstream of mill A <strong>and</strong> approximately 0.03-0.4% downstream of mill B. The<br />
chemistry data, along with MFO data, indicated that the fish sampled during the spring survey were exposed to<br />
mill effluent.<br />
Concurrent to the field surveys, laboratory effluent exposure tests were conducted to determine whether effluents<br />
from the <strong>Fraser</strong> River mills (Prince George <strong>and</strong> Quesnel mills) were capable of inducing MFO activity in<br />
exposed rainbow trout. Fish were exposed to 100% effluent for a total of four days. Hepatic EROD activity in<br />
exposed trout were induced 6.7-fold with mill A effluent, 8-fold with mill B effluent, 14.5-fold with mill C<br />
effluent <strong>and</strong> 3.1-fold with mill D effluent relative to reference fish.<br />
Similar exposure tests were conducted in the field at the mill A site using peamouth chub from the reference<br />
zone. Male <strong>and</strong> female chub were exposed to river water (collected upstream of diffuser) or 50% whole effluent<br />
from mill A for five days. After the exposure period MFO activity <strong>and</strong> circulating levels of testosterone were<br />
measured. Unfortunately, problems related to fish survival occurred (fungal infection) affecting the sample size,<br />
exposure time <strong>and</strong> power of the test. No differences were observed in EROD activity or plasma concentrations<br />
of testosterone between exposed <strong>and</strong> reference fish. Confidence in the results were influenced by high withintreatment<br />
variability <strong>and</strong> reduced exposure time. However, the on-site test represented a useful approach for<br />
assessing the potential of effluents to affect resident fish species, especially in situations where the capture<br />
success of exposed fish is poor.<br />
Despite the limited field data, there was evidence which suggested that effluent from mills A <strong>and</strong> B were capable<br />
of eliciting physiological responses in laboratory <strong>and</strong> resident fish species (immature chub). However, the<br />
success of using peamouth chub for monitoring the upper <strong>Fraser</strong> River is uncertain. First, peamouth chub is<br />
larger than many cyprinid/cottid species <strong>and</strong> its capacity for large-scale movement is unknown. Although likely<br />
to be less mobile relative to larger species such as mountain whitefish or squawfish, the degree of mobility of<br />
peamouth chub needs to be assessed. Second, the success of using peamouth chub as a sentinel monitoring<br />
species is strongly influenced by the ability to capture mature chub within the near-field zones. Unless capture<br />
success improves, use of peamouth chub as a sentinel species will be restricted to far-field zones, or mills located<br />
further downstream of Prince George where peamouth chub are more abundant.<br />
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