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FINAL REPORT - Grand River Conservation Authority

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<strong>Grand</strong> <strong>River</strong> Watershed-Wide Wastewater Optimization Pilot Project<br />

(kg/person/d)<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

Figure 11: Per capita TKN Loading<br />

typical median<br />

A B C D E F G H I J K L M N<br />

The following observations can be made concerning Figures 7 to 11:<br />

The median per capita flows for the 14 WWTPs surveyed (Figure 7) was 369<br />

L/person•d close to the typical value of 450 L/person•d. Two of the WWTPs<br />

(A and D) displayed evidence of inflow/infiltration as their per capita flows<br />

were above 500 L/person•d. One WWTP (Plant J) has very high per capita<br />

flows that are attributed to industrial discharges.<br />

For the ratio of peak day flow to annual average flow, Figure 8, the median<br />

value was 1.9. Four WWTPs (B,C, D and H) had ratios above 2.5. Plants A<br />

and D which had high per capita flows, did not have high ratios for peak day<br />

to annual average flow. This suggests that infiltration rather than inflow is the<br />

potential source of the higher per capita flows.<br />

For the per capita BOD 5 loadings, Figure 9, the median value for the WWTPs<br />

in the survey was 80 g/person•d, which is equal to the expected value of 80<br />

g/person•d. Plant E had a per capita BOD 5 loading twice that expected for a<br />

WWTP treating municipal discharges. During Workshop #3, operations staff<br />

identified that the WWTP is subject to significant industrial loads. Similarly,<br />

Plant J is known to have substantial BOD 5 loading from an industrial<br />

discharge. Plants C and I are small facilities using infrequent grab samples to<br />

32 | Page

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