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Wastewater Characterization of Fish Processing Plant Effluents

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efficient water use during low production days. Therefore, facilities with high daily<br />

production would have lower contaminant loading rates than indicated in Table 4.<br />

Table 4 Geometric Mean, Range and Average Contaminant Levels per Weight <strong>of</strong> <strong>Fish</strong> Processed<br />

Statistical Loading [kg/tonne]<br />

Facility Parameter BOD COD TSS NH -N<br />

4<br />

Average 24 75 14 9.3<br />

BC Packers Range 0.1 - 210 0.5 - 553 0.1 - 167 0.0 - 111<br />

Geo. Mean 7 18 4 0.7<br />

Average 15 4 14 0.1<br />

Bella Coola Range 0.7 - 69 3 - 6 0.6 - 69 0.02 - 0.1<br />

Geo. Mean 6 4 5 0.04<br />

Average 7 14 3 0.3<br />

Lions' Gate Range 0.6 - 28 3 - 39 0.5 - 10 0.1 - 0.5<br />

Geo. Mean 7 9 2 0.2<br />

Average 34 78 22 6.5<br />

Industry Range 0.1 - 1830 0.1 - 2575 0.1 - 1415 0.0 - 111<br />

Geo. Mean 6 9 3 0.4<br />

Variations in daily production, water use and waste concentration make it difficult to calculate<br />

precisely the amount <strong>of</strong> waste generated per unit <strong>of</strong> production. Geometric mean values for BC<br />

Packers, Bella Coola and Lions' Gate, and industry geometric mean values for other facilities,<br />

presented in Table 4 have been used to estimate annual contaminant loading to the Fraser River<br />

Estuary. It was not possible to estimate daily loadings based on month by month seasonal<br />

variations due to insufficient existing information.<br />

FREMP 03/21/1994<br />

<strong>Fish</strong> <strong>Processing</strong> <strong>Plant</strong> Effluent 89

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