Hidrológiai Közlöny 2006 (86. évfolyam)

3. szám - Kaposvári Kázmér: Effect of the intervening ozonizing and Biologie Activated Carbon treatmant to drinking water produced by water supply intake at the River Tisza Szolnok

26 HIDROLÓGIAI KÖZLÖNY 2006. 86. ÉVF. 3. SZ. MECHANICAL CLEANING, PRE-TREATMENT STANDBY WATER RESERVE WELL OZONE MIXING AND ABSORPTION BASINS Fig 1: The operational scheme of the Szolnok Surface Water Plant This paper does riot present and discuss the operative process control and quality measurement systems which are inseparable parts of the optimization of the purification plant. The adaptation of the new stages in to the process scheme was different from the standard arrangements in ca­se of the ozonizer only. The semiplant experiments drew the attention to the fact that the pre-ozone formed high residual organic matter, while the post-ozone - located right upstre­am of the activated carbon filter - regularly created secon­dary dispersed phase. These observations require the recon­sideration of the use of these methods. The interfacial oz­onization applied after the flocculation was promising in the achievement of the defined water quality targets. (Palicska J., 1989, Chedal J., 1982, Chedal J., 1985, Glaze W. H., 1990, DugnetJ. P., 1985) 4. The quality of the potable water after the commis­sioning of the enhanced process The values and limits in the MSZ 450-1/1989 Hungarian standard for the evaluation of the potable water parameters and the 21/2002. KöViM ministerial decree (effective from 1 s t April, 2003) are in compliance with the potable water re­quirements of the WHO and the EU. According to the re­sults of the auditory tests carried out by the concerned au­thorities, as well as the quality certifications provided by the operators; the treated, discharged water satisfies the require­ments even in respect of the earlier complained components and parameters ( Magyar P-né. - Palicska J. - Süveges GY. ­Kaposvári K., 2003). The consumers' complaints have also disappeared. The consumers recognized the "improvement" of the potable water. Besides the major consumers, who are in the knowledge of the quality parameters, a number of a­verage consumers have also indicated their favorable obser­vations. The sensible water quality improvement is steady, whereas the taste and odor effects in the raw and in the floc­culated Tisza water are still detectable. The ozonization and the activated carbon adsorption together ensure that the ma­terials responsible for the taste and odor observations re­main below the detection limits in the supplied water. After the ozonization, the iron and the manganese components are presented in an oxidized, precipitated form irrespectively from their original composition. Their concentration falls below the detection limit after the sand filtering. The break-through of the manganese in the purification system ­which was typical during the total freezing periods of the Tisza river - has totally disappeared. The reduction of the algae was spectacular. While the typical number of algae was between 10 4— 10 5 in the treated water before, presently we can steadily achieve 1 10 2— 5 10 2 e/L values (irrespective of the incoming number of algae) with the enhanced pro­cess. The frequency of occurrences between 1 10-1 10 4e/L is less than 2 %. The previous process was ineffective espe­cially against the micro algae, which problem has been sa­tisfactorily solved by the enhanced process. We can reduce the adverse consequences of the destruction of the alga cells - like the geosmin and the 2-MIB increase - with the inter­mittent injection of pre-chlorine and with using smaller than 0,5 g/m 3 dosage. The Daphnia tests show significant reduc­tion of the xenobiotic materials. The frequency of the previ­ously complained test results is zero. It must also be menti­oned that the typical 35 % insufficiency cases for the raw

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