Advances in Water Treatment and Enviromental Management
Advances in Water Treatment and Enviromental Management
Advances in Water Treatment and Enviromental Management
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RIBBLE ESTUARY WATER QUALITY IMPROVEMENTS 251works at a rate of 6DWF. Discharge flows <strong>in</strong> excess of those for the 1 <strong>in</strong> 5 year stormto sea via a short outfall (about 1 km) near the bath<strong>in</strong>g waters.For all these options it was necessary to determ<strong>in</strong>e the amount of storage that would berequired to limit the number of discharges from any comb<strong>in</strong>ed sewer overflows, to <strong>in</strong>l<strong>and</strong> ormar<strong>in</strong>e waters, to a frequency that would be acceptable <strong>in</strong> terms of general environmentalimpact, <strong>and</strong> <strong>in</strong> the case of those to sea to that which would not prejudice bath<strong>in</strong>g waterquality.Options for Treat<strong>in</strong>g Storm FlowsNorth bankFor Fairhaven, <strong>in</strong>vestigations concentrated on determ<strong>in</strong><strong>in</strong>g which storms would lead to spillsfrom the tanks outside the 3 hour period follow<strong>in</strong>g high water (the tidal w<strong>in</strong>dow), whendischarges receive maximum dilution <strong>and</strong> tend to move offshore away from the bath<strong>in</strong>g area.This <strong>in</strong>volved modell<strong>in</strong>g the effect, <strong>in</strong> terms of probable spill volumes, of all the time seriessummer storms, start<strong>in</strong>g at hourly <strong>in</strong>tervals through the tidal cycle. After comb<strong>in</strong><strong>in</strong>g some ofthe output to take account of similar spill volumes from different storms start<strong>in</strong>g at differenttidal states, an analysis of ra<strong>in</strong>fall data from nearby Blackpool airport (Head et al., <strong>in</strong> press)was used to determ<strong>in</strong>e the number of spills to be expected dur<strong>in</strong>g an average summer. FromFigure 5 it can be seen that <strong>in</strong>creas<strong>in</strong>g the exist<strong>in</strong>g storage from 10 000 m 3 to around 25 000m 3 would dramatically reduce the number of spills liable to occur. Above this figure thebenefit <strong>in</strong> terms of a reduction <strong>in</strong> the numbers of spills dim<strong>in</strong>ishes. Increas<strong>in</strong>g the tidal w<strong>in</strong>dowfrom 3 to 4 hours has a relatively small effect on spill frequency, whereas the removal of3DWF for treatment elsewhere would greatly reduce the number of spills.A much more limited exam<strong>in</strong>ation of the storm water management with regard to receiv<strong>in</strong>gwater quality was required <strong>in</strong> the case of Preston, as the <strong>in</strong>itial <strong>in</strong>vestigations showed that thebacterial loads from the comb<strong>in</strong>ed sewer overflows on the sewerage system only affected theupper <strong>and</strong> middle estuary, <strong>and</strong> that significant numbers of bacteria did not reach the bath<strong>in</strong>gareas.Figure 5 Relationships between storm water storage requirements <strong>and</strong> number ofdischarges dur<strong>in</strong>g an average summer for Fairhaven Tanks