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Proceedings - Teaching and Learning Centre - Simon Fraser ...

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<strong>Fraser</strong> River Action Plan 3rd Research Workshop<br />

pulp <strong>and</strong> paper mill effluent discharge rate to derive contaminant loadings in units of grams per day.<br />

These loadings were used to conduct model simulations.<br />

• Reported concentrations of 2,3,7,8-tetrachlorodibenzo-p-dioxin <strong>and</strong> 2,3,7,8-tetrachlorodibenzofuran in<br />

water, sediments <strong>and</strong> fish of the <strong>Fraser</strong> <strong>and</strong> Thompson rivers for the period of 1989 to 1993 were<br />

compiled. These data were used to verify model predictions <strong>and</strong> to derive model uncertainty.<br />

• An initial model verification was conducted by comparing available observed <strong>and</strong> predicted<br />

concentrations for the time period from 1989 to 1993. The results were compiled <strong>and</strong> are graphically<br />

illustrated in Figures 1 <strong>and</strong> 2.<br />

Figure 1 illustrates the agreement between observed <strong>and</strong> predicted concentrations of TCDF in the<br />

organic carbon of sediments at various locations in the <strong>Fraser</strong> <strong>and</strong> Thompson rivers. The quality of<br />

agreement between observed <strong>and</strong> predicted TCDF concentrations in river bed sediments can be<br />

expressed by the mean ratio of the observed <strong>and</strong> predicted concentrations of TCDF in the sediments,<br />

which is 1.33, suggesting the model slightly under-predicts the observed concentrations. The 95%<br />

confidence limits of the model predictions range by a factor of 1.7 of the mean, suggesting that 95% of<br />

the observed sediment concentrations are approximately within a factor of 1.7 of the predicted<br />

concentrations. The uncertainty introduced in the model due to year-to-year variability in monthly river<br />

flow rates, river compartment widths <strong>and</strong> depths, concentration in suspended sediments, organic carbon<br />

content of suspended sediments <strong>and</strong> water temperature is represented in Figure 1 by the error bars which<br />

are 95% confidence limits of the mean derived through Monte Carlo Simulation. The 95% confidence<br />

limits range between a factor of 1.0 to 2.3 of the mean among the various compartments in the <strong>Fraser</strong><br />

River <strong>and</strong> between a factor of 2.2 to 4.5 in the Thompson River. This means that year-to-year variability<br />

in the above mentioned model parameters is expected to cause variations in TCDF concentrations in the<br />

sediments that range between a factor of 2.0 to 4.5 depending on the location in the rivers. With the<br />

exception of the TCDF concentration observed in the <strong>Fraser</strong> River estuary (i.e., Compartment 18), all<br />

observed TCDF concentrations in the sediments of the <strong>Fraser</strong> <strong>and</strong> Thompson rivers are within the 95%<br />

confidence limits of the predicted concentrations. The higher TCDF concentration in the <strong>Fraser</strong> River<br />

estuary may be explained by local sources of TCDF, which are ignored in this study, as the <strong>Fraser</strong> River<br />

estuary is located in a highly industrialized part of Vancouver.<br />

Page 44

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