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Advances in Water Treatment and Enviromental Management

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Chapter 19DEVELOPMENTS IN IONEXCHANGE DENITRIFICATION: THE‘WASH-OUT’ PROCESSG S Solt (Cranfield Institute of Technology, UK), I J Fletcher(Hydrotechnica Ltd, Shewsbury, UK)SUMMARYIon exchange is at present the only denitrification process be<strong>in</strong>g <strong>in</strong>stalled <strong>in</strong> Brita<strong>in</strong>. There is much room forfurther improvement of the process, which suffers from several disadvantages. As development of ion exchangeby direct experimentation is extremely tedious, a computer simulation has been developed specifically forthis problem. It has led the way to an improved process for denitrify<strong>in</strong>g high-sulphate waters us<strong>in</strong>g conventionalType II anion res<strong>in</strong>, which appears to compete favourably with the use of nitrate-selective res<strong>in</strong>. The processdepends on the rapid change <strong>in</strong> the res<strong>in</strong>’s aff<strong>in</strong>ity for polyvalent ions with chang<strong>in</strong>g concentration <strong>in</strong> theliquid. Further development cont<strong>in</strong>ues.1. HISTORICAL BACKGROUNDIn recent decades nitrate levels <strong>in</strong> groundwater sources have been ris<strong>in</strong>g steadily <strong>in</strong> many areas, largely asthe result of modern agricultural methods, though there has been fierce dispute just how this comes about.In Brita<strong>in</strong> these disputes have for long obscured the essential issue alternative methods of lower<strong>in</strong>g nitratelevels <strong>in</strong> order to meet the EEC Directive on potable water hav<strong>in</strong>g been exhausted, many groundwatersources now require denitrification. Whatever changes are made <strong>in</strong> agriculture, the number of such sourcesis likely to go on <strong>in</strong>creas<strong>in</strong>g over the next few years at least.In Brita<strong>in</strong>, all denitrification plants currently be<strong>in</strong>g built or designed are based on anion exchange. Ionexchange has the advantage of be<strong>in</strong>g a well-tried <strong>in</strong>dustrial process rais<strong>in</strong>g no novelty <strong>in</strong> eng<strong>in</strong>eer<strong>in</strong>g orcontrol. Biological or membrane processes may be used <strong>in</strong> future, but at present fall short on comb<strong>in</strong>edconsiderations of cost, treated water quality, reliability <strong>and</strong> ease of operation.In the ion exchange process water passes through a column of anion exchange res<strong>in</strong> <strong>in</strong> the chloride (orchloride/bicarbonate) form. The res<strong>in</strong> has a higher aff<strong>in</strong>ity for nitrate ions <strong>and</strong> takes them up <strong>in</strong> exchangefor chloride (<strong>and</strong> bicarbonate). When its capacity is exhausted, the unit is taken out of service <strong>and</strong> regeneratedwith br<strong>in</strong>e (or br<strong>in</strong>e <strong>and</strong> bicarbonate).2. PROBLEMS OF ANION EXCHANGE DENITRIFICATIONWhile its eng<strong>in</strong>eer<strong>in</strong>g is conventional, the process presents some chemical problems when put to this purpose:a) Conventional anion exchange res<strong>in</strong> has an aff<strong>in</strong>ity for sulphate which is even higher than for nitrate,so that sulphate is also removed, wast<strong>in</strong>g res<strong>in</strong> capacity <strong>and</strong> regenerat<strong>in</strong>g chemicals.b) Replacement by chloride, of sulphate, nitrate <strong>and</strong> some of the bicarbonate <strong>in</strong> the raw water <strong>in</strong>creasesthe chloride: bicarbonate ratio <strong>in</strong> the product, <strong>and</strong> <strong>in</strong> many cases results <strong>in</strong> a corrosive water.© 1991 Elsevier Science Publishers Ltd, Engl<strong>and</strong><strong>Water</strong> <strong>Treatment</strong>—Proceed<strong>in</strong>gs of the 1st International Conference, pp. 191–198191

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