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Advances in Water Treatment and Enviromental Management

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250 WATER TREATMENTFigure 4. Effects comb<strong>in</strong>ed discharges from Preston <strong>and</strong> Fairhaven follow<strong>in</strong>g variouslevels of bacterial removal. Dispersion model simulations, E. coli concentrationsgreater than 2 000 per 100 ml: a 95 per cent removal, b 99 per cent removal.South bankThe exist<strong>in</strong>g dra<strong>in</strong>age system for Southport is designed to convey flows of comb<strong>in</strong>ed foul <strong>and</strong>storm sewage for primary treatment at a works discharg<strong>in</strong>g via Crossens Pool to the Ribbleestuary. Although the effluent from this works comprises a large proportion of the flow <strong>in</strong>Crossens Pool, lead<strong>in</strong>g to local oxygen depletion problems, particularly <strong>in</strong> the summer, itseffects on bath<strong>in</strong>g water quality are small. Inadequate capacity of the exist<strong>in</strong>g sewerage systemleads to premature operation of exist<strong>in</strong>g comb<strong>in</strong>ed sewer overflows <strong>and</strong> the flood<strong>in</strong>g ofproperties. In plann<strong>in</strong>g improvements to the system to alleviate these problems, it wasnecessary to determ<strong>in</strong>e how best to deal with the base flow so that the effects of discharges ofstorm water on bath<strong>in</strong>g water quality could be reduced to a level compatible with therequirements of the Bath<strong>in</strong>g <strong>Water</strong> Directive. S<strong>in</strong>ce only part of the system <strong>in</strong>volves comb<strong>in</strong>edoverflows discharg<strong>in</strong>g to areas near the bath<strong>in</strong>g waters, it was necessary to consider convey<strong>in</strong>gdifferent multiples of the base flow to the site of the exist<strong>in</strong>g works, depend<strong>in</strong>g on whether theoverflows were to <strong>in</strong>l<strong>and</strong> water courses or to the sea. Additionally the possibility ofconstruct<strong>in</strong>g a long sea outfall for some or all of the base or storm flows needed to beconsidered. After tak<strong>in</strong>g <strong>in</strong>to account the various constra<strong>in</strong>ts associated with exist<strong>in</strong>g l<strong>and</strong>use <strong>and</strong> obta<strong>in</strong><strong>in</strong>g permissions for new constructions it was possible to narrow the options tobe considered to:convey all flows up to a 1 <strong>in</strong> 5 year storm, from areas where overflows would need tobe to the sea, to the exist<strong>in</strong>g sewage works site. Allow volumes <strong>in</strong> excess of these tobe discharged via a relatively short outfall (about 1 km) near the bath<strong>in</strong>g waters. Forareas with overflows to <strong>in</strong>l<strong>and</strong> water courses, transfer approximately 6DWF to theexist<strong>in</strong>g sewage works site. Discharge flows <strong>in</strong> excess of 6DWF arriv<strong>in</strong>g at the worksvia an overflow to Crossens Pool;convey all flows from areas where overflows would need to be to the sea to a coastalsite for pretreatment <strong>and</strong> possibly storage before discharg<strong>in</strong>g to the sea. Dischargevolumes up to a 1 <strong>in</strong> 5 year storm via a long outfall (about 4.5 km) <strong>and</strong> those <strong>in</strong>excess of this via a short outfall (about 1 km) near the bath<strong>in</strong>g waters. Transfer flowsof up to 6DWF from <strong>in</strong>l<strong>and</strong> areas to the exist<strong>in</strong>g sewage works site;convey flows up to 6DWF from all areas to the exist<strong>in</strong>g sewage works site. Dischargeflows of between 6DWF <strong>and</strong> a 1 <strong>in</strong> 5 year storm via a long sea outfall (about 4.5 km),with or without storage to limit the time of the discharge; or store <strong>and</strong> transfer to the

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