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Advances in Water Treatment and Enviromental Management

Advances in Water Treatment and Enviromental Management

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194 WATER TREATMENTFIGURE 1 NITRATE CAPACITYThe graph shows the res<strong>in</strong>’s work<strong>in</strong>g capacity with respect to nitrate only. The conventional res<strong>in</strong> normallyhas a low nitrate capacity because it uses up much of its work<strong>in</strong>g capacity <strong>in</strong> remov<strong>in</strong>g the sulphate <strong>in</strong> thewater as well. The conventional res<strong>in</strong> performs relatively badly at the low regeneration level, which is themost economical <strong>in</strong> terms of regenerant usage.This water calls for br<strong>in</strong>e <strong>and</strong> bicarbonate regeneration to give the f<strong>in</strong>al blended product the desiredchloridetbicarbonate ratio. Two po<strong>in</strong>ts have been superimposed which show the reduced regeneration efficiencydue to lower effectiveness of bicarbonate as a regenerant as compared with chloride. On these po<strong>in</strong>ts thebicarbonate wash represented 10% <strong>and</strong> 25% respectively of the total regeneration levelThe graph also shows two “Washout” results for br<strong>in</strong>e/bicarbonate regeneration <strong>in</strong> which the bicarbonateaccounted for 40% of the total regeneration level. Washout was performed with 10 bed volumes of 8 eq/1sulphate solution. Their results suggest that on this raw water analysis the process br<strong>in</strong>gs the conventionalres<strong>in</strong>’s performance with bicarbonate regeneration to the same level as that of the selective res<strong>in</strong>s, at leastat the low regeneration levels which have so far been explored.This set of process details was determ<strong>in</strong>ed by an exhaustive computer simulation. Its predictions weretested first on a made-up water <strong>in</strong> the laboratory <strong>and</strong> then on the actual water <strong>in</strong> the field. The resultssuggested that the Washout process with co-flow regeneration of conventional res<strong>in</strong> has a lower operat<strong>in</strong>gcost (<strong>in</strong> terms of regenerant usage) than conventional operation of the nitrate-selective res<strong>in</strong>.In this case the eluates from the actual regeneration by chloride <strong>and</strong> bicarbonate are both completelyreta<strong>in</strong>ed for use as washout <strong>in</strong> the next cycle. Apart from relatively clean streams such as backwash <strong>and</strong>r<strong>in</strong>se, only the washout step eluate has to be disposed of, <strong>and</strong> this conta<strong>in</strong>s mostly nitrate <strong>and</strong> sulphate.The results shown <strong>in</strong> Figure 1 are field results. The field trials varied considerably from run to run (as ionexchange processes tend to do) but when averaged, the results confirm the computer’s predictions shown <strong>in</strong>Table 2. Table 2 also compares the use of a conventional res<strong>in</strong> with Washout, with that of a selective res<strong>in</strong><strong>in</strong> the normal manner. The criteria for these tests where that the nitrate level of the blended product shouldnot exceed 0.8 mg equiv 1 -1 , <strong>and</strong> that its chloride:bicarbonate ratio should not rise above 0.5.Figure 2 shows the analyses of blended product water produced by these two processes. The last two l<strong>in</strong>es<strong>in</strong> each half of Table 2 give the waste volume <strong>and</strong> the total ions discharged by the respective processes.While the Washout process produces a far greater volume, its total salt content, <strong>and</strong> especially its chloridecontent, is much smaller.

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