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  • About
  • The Global ETD Search service is a free service for researchers to find electronic theses and dissertations. This service is provided by the Networked Digital Library of Theses and Dissertations.
    Our metadata is collected from universities around the world. If you manage a university/consortium/country archive and want to be added, details can be found on the NDLTD website.
1

Efekti odabranih unapredenih procesa oksidacije i koagulacije na sadržaj prirodnih organskih materija u vodi / The effects of selected advanced oxidation processes and coagulation on natural organic matter content in water

Molnar Jazić Jelena 10 October 2011 (has links)
<p>Cilj ovog rada bio je da se u laboratorijskim uslovima ispitaju efekti odabranih<br />unapredenih procesa oksidacije (Fenton proces, ozonizacija, TiO2-katalizovana ozonizacija,<br />perokson proces i TiO2-katalizovan perokson proces) i koagulacije na sadržaj i strukturu<br />prirodnih organskih materija u vodi, kao prekursora dezinfekcionih nusprodukata hlora.<br />Karaterizacija POM frakcionisanjem pre i nakon navedenih oksidacionih tretmana i<br />koagulacije izvr&scaron;ena je u cilju ispitivanja mehanizama oksidacije i uklanjanja POM, kao i<br />utvrdivanja promene reaktivnosti prekursorskog materijla DBP (trihalometana i halosircetnih<br />kiselina, kao najvi&scaron;e zastupljenih DBP, i haloacetonitrila, hlorpikrina i haloketona, kao<br />nedovoljno istraženih, visoko prioritetnih &bdquo;DBP u razvoju&ldquo;).<br />Analizom hemijskih karakteristika prirodnog matriksa utvrdeno je da voda sadrži<br />visoke koncentracije prirodnih organskih materija (DOC sirove iznosi 9,92&plusmn;0,87 mg/L) uz<br />dominaciju materija hidrofobnog karaktera (14% huminskih i 65% fulvinskih kiselina). U<br />slucaju sintetickog matriksa (sadržaj DOC 11,2&plusmn;0,37 mg/L) zastupljena je samo frakcija<br />huminske kiseline, te je iz tog razloga sinteticki matriks znatno hidrofobniji u odnosu na<br />prirodni. Veci stepen hidrofobnosti sintetickog matriksa u poredenju sa prirodnim matriksom,<br />rezultovao je i vecim sadržajem prekursora najzastupljenijih dezinfekcionih nusprodukata<br />hlora, THM i HAA. Vrednosti za PFTHM iznose 438&plusmn;88,2 &mu;g/L za prirodni matriks,<br />odnosno 3646&plusmn;41,3 &mu;g/L za sinteticki matriks, dok PFHAA prirodnog matriksa iznosi<br />339&plusmn;68,9 &mu;g/L, odnosno 559&plusmn;20,5 &mu;g/L za sinteticki matriks. Sadržaj HAN, CP i HK je<br />znatno niži u poredenju sa prekursorima THM i HAA. PFHAN iznosi 3,65 &mu;g/L za prirodni,<br />odn. 7,98 &mu;g/L za sinteticki matriks, dok prekursori CP nisu detektovani. Prekursori HK su<br />zastupljeni samo u strukturi POM prirodnog matriksa i PFHK iznosi 46,9&plusmn;5,08 &mu;g/L.<br />Hidrofoban materijal, kao dominantan u strukturi POM ispitivanih matriksa, je ujedno i<br />osnovni prekursorski materijal THM i HAA, dok su prekursori haloacetonitrila i haloketona u<br />navecoj meri zastupljeni u hidrofilnoj frakciji.<br />Ispitivanjem uticaja Fenton procesa na sadržaj POM, pri optimalnim reakcionim<br />uslovima (pH 5, reakciono vreme od 15 min. i brzina me&scaron;anja 30 o/min), postignuto je u<br />zavisnosti od primenjene doze Fe2+, molarnog odnosa Fe2+ i H2O2 i matriksa 80-95%<br />smanjenja saržaja DOC, 70-99% PFTHM, 37-92% PFHAA. Kao posledica uklanjanja POM<br />oksidaciojom i koagulacijom, zabeležene su blage fluktuacije u sadržaju prekursora HAN, CP<br />i HK.<br />Ispitivanjem uticaja ozonizacije u vodi pri razlicitim pH na sadržaj i strukturu POM<br />utvrdeno je da je ozonizacija u baznoj sredini efikasnija za uklanjanje POM u odnosu na<br />ozonizaciju u kiseloj sredini. Katalizovanje procesa ozonizacije primenom TiO2 u vodi<br />razlicitim pH unapreduje smanjenje sadržaja kako ukupnih organskih materija, tako i<br />specificnih prekursora DBP u poredenju sa ozonizacijom. Najefikasnije smanjenje sadržaja<br />POM postignuto je TiO2-O3 procesa u baznoj sredini primenom 3,0 mg O3/mg DOC i 1,0 mg<br />TiO2/L (30% DOC, 92-100% PFTHM, PFHAA, PFHAN i PFHK). TiO2-O3 proces pri svim<br />pH vrednostima produkuje manji sadržaj CP u odnosu na ozonizaciju. Veca efikasnost<br />primenjenih procesa u smanjenju sadržaja POM sintetickog matriksa u odnosu na prirodni<br />ukazuju da je frakcija huminske kiseline podložnija oksidacionom tretmanu u odnosu na<br />fulvinsku, kao dominantnu frakciju POM prirodnog matriksa. Kada je u pitanju mehanizam<br />oksidacije POM ispitivanih matriksa, primenom ozonizacije i TiO2-O3 procesa, pri svim pH<br />postignuta je potpuna oksidacija frakcije huminske kiseline do fulvinske kiseline i hidrofilnih<br />jedinjenja. U slucaju ozonizacije, sa povecanjem pH vrednosti sredine, usled povecane<br />produkcije hidroksil radikala iz ozona, povecao se i udeo odnosno sadržaj DOC u hidrofilnoj<br />frakciji ozonirane vode (86%-90%). Raspodela DOC nakon TiO2-O3 procesa pri svim pH<br />vrednostima je oko 70% i 50% u hidrofilnoj frakciji prirodnog i sintetickog matriksa, redom.<br />Frakcija koja se dominantno formira nakon navedenih oksidacionih tretmana je hidrofilna nekisela<br />frakcija. Frakcionisanjem POM nakon oksidacionih tretmana je utvrdeno da su<br />prekursori THM i HAA kako hidrofobne aromaticne strukture, tako i hidrofilna polarna<br />jedinjenja, dok je najreaktivniji prekursorski materijal HAN, CP i HK sadržan u hidrofilnoj<br />frakciji POM.<br />Uvodenjem H2O2 u proces ozonizacije (O3/H2O2 i iO2-O3/H2O2) u slabo baznoj<br />sredini (pH 7-7,5) postignut je jo&scaron; veci stepen oksidacije POM i povecanje udela hidrofilnih<br />struktura (oko 88%) ispitivanih matriksa u odnosu na ozonizaciju i iO2-O3 (oko 70%),<br />primenom 3,0 mg O3/mg DOC; O3:H2O2=1:1 i 1,0 mg iO2/L. Povecanje sadržaja prekursora<br />THM i HAA samo u slucaju prirodnog amtriksa posledica je povecanja reaktivnosti frakcije<br />fulvinske kiseline nakon O3/H2O2 i iO2-O3/H2O2 procesa, u kojoj su ujedno i prekursori HK<br />najzastupljeniji. Najveci sadržaj azotnih DBP (HAN i CP) sadrži hidrofilna frakcija POM.<br />Ispitivanjem kombinovanih procesa ozonizacije i TiO2-O3 i koagulacije utvrdeno je da<br />oksidacioni tretmani imaju pozitivne efekte u uklanjaju POM koagulacijom. Maksimalna<br />efikasnost smanjenja sadržaja DOC od 32% postignuto je primenom 3,0 mg O3/mg DOC i<br />200 mg FeCl3/L, dok su ne&scaron;to niže doze ozona pogodne za uklanjanje prekursora DBP (80-<br />89% PFTHM, PFHAA, PFHAN i PFHK, primenom 0,7-1,0 mg O3/mg DOC i 200 mg<br />FeCl3/L). Prekursori CP koji se formiraju ozonizacijom zaostaju u vodi nakon koagulacije.<br />Rezultati dobijeni tokom istraživanja ukazuju da se primenom razlicitih oksidacionih i<br />unapredenih oksidacionih procesa može smanjiti sadržaj POM i prekursora DBP do<br />odredenog stepena. Kao najefikasniji u uklanjaju kako ukupnih organskih materija, tako i<br />specificih prekursora DBP se pokazao Fenton proces. Kada su u pitanju unapredeni procesi<br />oksidacije zasnovani na primeni ozona, uvodenje katalizatora ili H2O2 kao oksidanta u proces<br />ozonizacije, kao i odabir optimalne pH vrednosti procesa može unaprediti oksidabilnost<br />organskih molekula. Pri tom, poznavanje mehanizama oksidacije POM iz razlicitih izvora<br />primenom ozona i/ili hidroksil radikala, kao i mehanizma uklanjanja POM koagulacijom<br />može se primeniti za odabir i optimizovanje odgovarajuceg procesa u tretmanu vode za pice,<br />a u zavisnosti od kvaliteta sirove vode.</p> / <p>The aim of this work was to examine under laboratory conditions the effects of<br />certain advanced oxidation processes (Fenton process, ozonation, TiO2-catalyzed ozonation,&nbsp;peroxone process and TiO2-catalyzed peroxone process) and coagulation on the content,&nbsp;structure and role of natural organic matter in water as the precursors of chlorine disinfection&nbsp;byproducts. The NOM was characterized by fractionation before and after these oxidation&nbsp;treatments and coagulation, in order to investigate NOM oxidation mechanisms and identify&nbsp;the changes in the reactivity of DBP precursor material (trihalomethanes and haloacetic acids,&nbsp;as the most abundant DBP, and haloacetonitriles, chloropicrin and haloketones, as underresearched,&nbsp;high priority &ldquo;emerging DBP&rdquo;).&nbsp;Through analysis of the chemical characteristics of the natural matrix, it was found&nbsp;that the water contains high concentrations of natural organic matter (raw water DOC was&nbsp;9.92 &plusmn; 0.87 mg/L) dominated by substances with a hydrophobic character (14% humic and&nbsp;65% fulvic acids). The synthetic matrix studied (DOC content of 11.2 &plusmn; 0.37 mg/L)&nbsp;contained only the humic acid fraction, and was therefore significantly more hydrophobic&nbsp;compared to the natural one. The greater degree of hydrophobicity in the synthetic matrix&nbsp;relative to the natural matrix resulted in a higher content of precursors of the most frequent&nbsp;chlorine disinfection byproducts, THM and HAA. The THMFP of the natural matrix was&nbsp;438&plusmn;88.2 mg/L, compared to 3646&plusmn;41.3 mg/L for the synthetic matrix, while the HAAFP of&nbsp;the natural matrix was 339&plusmn;68.9 mg/L, compared to 559&plusmn;20.5 mg/L for the synthetic matrix.&nbsp;The contents of HAN, CP, and HK precursors were much lower than the THM and HAA&nbsp;precursors. HANFP were 3.65 mg/L for natural, and 7.98 mg/L for the synthetic matrix,&nbsp;whilst CP precursors were not detected. HK precursors were present only in the structure of&nbsp;the natural NOM matrix, with a HKFP of 46.9&plusmn;5.08 mg/L. Hydrophobic material, as the&nbsp;dominant structure in the investigated NOM matrix, is the basic precursor material of THM&nbsp;and HAA, while the precursors of haloacetonitriles and haloketones are represented mostly in&nbsp;the hydrophilic fraction.<span style="font-size: 12px;">Whilst examining the influence of the Fenton process on the NOM content, under&nbsp;</span><span style="font-size: 12px;">optimal reaction conditions (pH 5, reaction time of 15 min and stirring speed of 30 rpm),&nbsp;</span><span style="font-size: 12px;">depending upon the applied dose of Fe2+, the molar ratio of Fe2+ and H2O2, and the matrix,&nbsp;</span><span style="font-size: 12px;">reductions in the DOC content of 80-95%, in the THMFP of 70-99%, and in the HAAFP of&nbsp;</span><span style="font-size: 12px;">37-92%, were achieved. As a result of removing NOM by oxidation and coagulation, mild&nbsp;</span><span style="font-size: 12px;">fluctuations in the contents of HAN, CP and HK precursors were recorded.&nbsp;</span><span style="font-size: 12px;">The investigation into the effects of ozonation at different pH levels on the content&nbsp;</span><span style="font-size: 12px;">and structure of NOM has shown that ozonation under alkaline conditions is more effective at&nbsp;</span><span style="font-size: 12px;">removing NOM than ozonation under acidic conditions. Catalyzing the ozonation process&nbsp;</span><span style="font-size: 12px;">using TiO2 in water with different pH promotes the reduction of both total organic matter and&nbsp;</span><span style="font-size: 12px;">specific DBP precursors in comparison with ozonation alone. The most effective NOM&nbsp;</span><span style="font-size: 12px;">reduction was achieved using the TiO2-O3 process in alkaline conditions using 3.0 mg O3/mg&nbsp;</span><span style="font-size: 12px;">DOC and 1.0 mg TiO2/L (30% DOC, 92-100% THMFP, HAAFP, HANFP and HKFP). The&nbsp;</span><span style="font-size: 12px;">TiO2-O3 process produces lower amounts of CP at all pH values, relative to ozonation. The&nbsp;</span><span style="font-size: 12px;">applied processes showed increased efficacy in reducing the NOM content of the synthetic&nbsp;</span><span style="font-size: 12px;">matrix compared with the natural matrix, which shows that the humic acids fraction is more&nbsp;</span><span style="font-size: 12px;">susceptible to oxidation treatments than the fulvic acids which are the dominant faction of the&nbsp;</span><span style="font-size: 12px;">natural NOM matrix. Regarding the NOM oxidation mechanism in the investigated matrices,&nbsp;</span><span style="font-size: 12px;">using ozonation and the TiO2-O3 process, complete oxidation of the humic acid fraction to&nbsp;</span><span style="font-size: 12px;">fulvic acids and hydrophilic compounds was achieved at all pH levels. In the case of&nbsp;</span><span style="font-size: 12px;">ozonation, increasing the pH in the matrix lead to an increase in hydroxyl radicals production&nbsp;</span><span style="font-size: 12px;">from ozone, and the proportion or content of DOC in the hydrophilic fraction of ozonated&nbsp;</span><span style="font-size: 12px;">water (86%-90%) increased. The distribution of DOC after the TiO2-O3 process at all pH&nbsp;</span><span style="font-size: 12px;">values was about 70% and 50% in the hydrophilic fraction of the natural and synthetic&nbsp;</span><span style="font-size: 12px;">matrices, respectively. The dominant fraction formed after the oxidation treatments was the&nbsp;</span><span style="font-size: 12px;">hydrophilic non-acid fraction. By NOM fractionation after the oxidation treatments, it was&nbsp;</span><span style="font-size: 12px;">shown that the THM and HAA precursors are hydrophobic aromatic structures and&nbsp;</span><span style="font-size: 12px;">hydrophilic polar compounds, whilst the most reactive precursor materials for HAN, CP and&nbsp;</span><span style="font-size: 12px;">HC are contained in the hydrophilic NOM fraction.&nbsp;</span><span style="font-size: 12px;">Introducing H2O2 into the ozonation process (O3/H2O2 and iO2-O3/H2O2) in weak&nbsp;</span><span style="font-size: 12px;">basic conditions (pH 7 to 7.5) enhances further the degree of NOM oxidation and increases&nbsp;</span><span style="font-size: 12px;">the proportion of hydrophilic structures (88%) in the examined matrices in comparison to&nbsp;</span><span style="font-size: 12px;">ozonation and iO2-O3 (about 70%), using 3.0 mg O3/mg DOC; O3:H2O2=1:1 and 1.0 mg&nbsp;</span><span style="font-size: 12px;">iO2/L. An increase in the THM and HAA precursor contents occurred in the case of the&nbsp;</span><span style="font-size: 12px;">natural matrix as a result of the increased reactivity of the fulvic acid fraction after the&nbsp;</span><span style="font-size: 12px;">O3/H2O2 and iO2-O3/H2O2 processes, and HK precursors were also present. The highest&nbsp;</span><span style="font-size: 12px;">content of nitrogen DBP (HAN and CP) was found in the hydrophilic NOM fraction.&nbsp;</span><span style="font-size: 12px;">By examination of the combined processes of ozonation, TiO2-O3 and coagulation, it was&nbsp;</span><span style="font-size: 12px;">shown that oxidative treatments have a positive effect on NOM removal by coagulation. A&nbsp;</span><span style="font-size: 12px;">maximum efficacy in reducing DOC by 32% was achieved with 3.0 mg O3/mg DOC and&nbsp;</span><span style="font-size: 12px;">200 mg FeCl3/L, whereas slightly lower ozone doses are suitable for the removal of DBP&nbsp;</span><span style="font-size: 12px;">precursors (80-89% THMFP, HAAFP, HANFP and HKFP, using 0.7-1.0 mg O3/mg DOC&nbsp;</span><span style="font-size: 12px;">and 200 mg FeCl3/L). CP precursors which are formed during ozonation remain in the water&nbsp;</span><span style="font-size: 12px;">after coagulation.&nbsp;</span><span style="font-size: 12px;">The results obtained during this investigation show that the application of different oxidation&nbsp;</span><span style="font-size: 12px;">and enhanced oxidation processes can reduce the contents of NOM and DBP precursors to&nbsp;</span><span style="font-size: 12px;">some degree. The most effective process at removing both total organic matter and specific&nbsp;</span><span style="font-size: 12px;">DBP precursors proved to be the Fenton process. With respect to enhanced oxidation&nbsp;</span><span style="font-size: 12px;">processes based upon the use of ozone, by introducing catalysts or H2O2 as an oxidant in the&nbsp;</span><span style="font-size: 12px;">ozonation process and by selecting the optimum pH for the process, the oxidizability of&nbsp;</span><span style="font-size: 12px;">organic molecules can be improved. In addition, knowledge of the NOM oxidation&nbsp;</span><span style="font-size: 12px;">mechanisms from different sources using ozone and / or hydroxyl radicals, as well as the&nbsp;</span><span style="font-size: 12px;">mechanism of NOM removal by coagulation, can be used to select and optimize the most&nbsp;</span><span style="font-size: 12px;">appropriate process in drinking water treatment, depending upon the quality of the raw water.</span></p>
2

Uticaj oksidacionih procesa na bazi ozona, vodonik-peroksida i UV zračenja na sadržaj i reaktivnost prirodnih organskih materija u vodi / The influence of oxidation processes based on ozone, hydrogen peroxide and UV irradiation on the content and reactivity of natural organic matter in water

Petronijević Mirjana 28 August 2019 (has links)
<p>Cilj&nbsp; istraživanja&nbsp; u&nbsp; okviru&nbsp; ove&nbsp; doktorske&nbsp; disertacije&nbsp; je&nbsp; utvrđivanje&nbsp; efekata&nbsp; različitih<br />oksidacionih procesa na bazi ozona, vodonik-peroksida i UV zračenja na sadržaj i reaktivnost prirodnih&nbsp; organskih&nbsp; materija&nbsp; (POM)&nbsp; u&nbsp; različitim&nbsp; vodenim&nbsp; matriksima.&nbsp; Ispitivanja&nbsp; su sprovedena&nbsp; na&nbsp; a)&nbsp; podzemnoj&nbsp; vodi&nbsp; sa&nbsp; teritorije&nbsp; Kikinde&nbsp; i&nbsp; Temerina&nbsp; (prirodni&nbsp; matriks)&nbsp; i&nbsp; b) sintetičkom&nbsp; vodenom&nbsp; matriksu&nbsp; (rastvoru&nbsp; komercijalno&nbsp; dostupne&nbsp; huminske&nbsp; kiseline),&nbsp; koji&nbsp; se među sobom razlikuju po sastavu i strukturi prisutne POM i sadržaju bromida. Za oksidacioni proces&nbsp; (ozonizacija,&nbsp; UV&nbsp; fotoliza,&nbsp; oksidacija&nbsp; sa&nbsp; H<sub> 2</sub>O<sub>2</sub>,&nbsp; kombinovani&nbsp; O <sub>3 </sub>/UV&nbsp; proces&nbsp; i kombinovani&nbsp; H <sub>2</sub>O<sub>2</sub><br />/UV&nbsp; proces)&nbsp; pojedinačno&nbsp; ispitan&nbsp; je&nbsp; uticaj&nbsp; različitih&nbsp; doza&nbsp; oksidanata&nbsp; i reakcionih&nbsp; uslova.Posebna&nbsp; pažnja&nbsp; posvećena&nbsp; je&nbsp; ispitivanju&nbsp; uticaja&nbsp; navedenih&nbsp; tretmana&nbsp; na<br />formiranje&nbsp; neorganskog&nbsp; bromata,&nbsp; kao&nbsp; i&nbsp; uticaja&nbsp; na&nbsp; sadržaj&nbsp; prekursora&nbsp;&nbsp; dezinfekcionih nusproizvoda nakon hlorisanja (THM, HAA, HAN, HK i CP).<br />Analiza&nbsp; hemijskih&nbsp; parametara&nbsp; sintetičkog&nbsp; matriksa&nbsp; (5,44&plusmn;0,30&nbsp; mg&nbsp; C/l; 0,255&plusmn;0,015 cm<sup> -1</sup> ;&nbsp; 4,68&plusmn;0,41&nbsp; lm<sup> -1</sup> mg <sup>-1 </sup>)&nbsp; pokazuje&nbsp; da&nbsp; u&nbsp; njemu&nbsp; preovladavaju&nbsp; huminnske materije&nbsp; visoke&nbsp; hidrofobnosti.&nbsp; Visok&nbsp; sadržaj&nbsp; POM&nbsp; pretežno&nbsp; hidrofobnog&nbsp; karaktera&nbsp; je zabeležen i u vodi iz Kikinde (5,170,72 mg C/l; 0,2010,001 cm <span id="cke_bm_192S" style="display: none;">&nbsp;</span><span id="cke_bm_190S" style="display: none;">&nbsp;</span><sup>-1</sup><span id="cke_bm_192E" style="display: none;">&nbsp;</span><span id="cke_bm_190E" style="display: none;">&nbsp;</span> ; 3,88&plusmn;0,70 lm<span id="cke_bm_193S" style="display: none;">&nbsp;</span><sup> -1</sup><span id="cke_bm_193E" style="display: none;">&nbsp;</span> mg<sup> -1</sup> ), dok je&nbsp; sadrža<span id="cke_bm_194E" style="display: none;">&nbsp;</span>j&nbsp; POM&nbsp; u&nbsp; sirovoj&nbsp; vodi&nbsp; iz&nbsp; Temerina&nbsp; (2,060,38&nbsp; mg&nbsp; C/l;&nbsp; 0,0500,001&nbsp; cm<span id="cke_bm_203S" style="display: none;">&nbsp;</span><span id="cke_bm_201S" style="display: none;">&nbsp;</span><sup> -1</sup><span id="cke_bm_203E" style="display: none;">&nbsp;</span><span id="cke_bm_201E" style="display: none;">&nbsp;</span>&nbsp; ; 2,43&plusmn;0,21 lm <span id="cke_bm_204S" style="display: none;">&nbsp;</span><sup>-1</sup><span id="cke_bm_204E" style="display: none;">&nbsp;</span> mg <sup>-1</sup><span id="cke_bm_205E" style="display: none;">&nbsp;</span><span id="cke_bm_202E" style="display: none;">&nbsp;</span><span id="cke_bm_191E" style="display: none;">&nbsp;</span><br />) značajno niži i preovladavaju POM hidrofilnog karaktera. Veći stepen hidrofobnosti sintetičkog matriksa u poređenju sa&nbsp; prirodnim matriksima, rezultovao&nbsp; je&nbsp; i&nbsp; većom&nbsp; reaktivnosti&nbsp; organske&nbsp; materije&nbsp; sa&nbsp; hlorom,&nbsp; &scaron;to&nbsp; se&nbsp; može&nbsp; zaključiti&nbsp; na<br />osnovu visokih vrednosti PFDBP nakon hlorisanja. Vrednost PFTHM u sintetičkom matriksu iznosi&nbsp; 544&plusmn;85,9&nbsp; &micro;g/l,&nbsp; dok&nbsp; je&nbsp; PFTHM&nbsp; u&nbsp; kikindskoj&nbsp; i&nbsp; temerinskoj&nbsp; sirovoj&nbsp; vodi&nbsp; znatno&nbsp; niži (279&plusmn;32,3&nbsp; i&nbsp; 180&plusmn;44,0&nbsp; &micro;g/l,&nbsp; respektivno).&nbsp; Vrednost&nbsp; PFHAA&nbsp; u&nbsp; sintetičkom&nbsp; matriksu&nbsp; iznosi 484&plusmn;77,5 &micro;g/l, dok je PFHAA u kikindskoj 244&plusmn;11,1 &micro;g/l i u temerinskoj vodi 165&plusmn;32,5 &micro;g/l. Sadržaj&nbsp; HK&nbsp; (8,05&plusmn;3,63&nbsp; &micro;g/l&nbsp; sintetički&nbsp; matriks;&nbsp; 14,91,38&nbsp; &micro;g/l&nbsp; Kikinda;&nbsp; 7,400,25&nbsp; &micro;g/l Temerin)&nbsp; je&nbsp; znatno&nbsp; niži&nbsp; u&nbsp; poređenju&nbsp; sa&nbsp; prekursorima&nbsp; THM&nbsp; i&nbsp; HAA,&nbsp; dok&nbsp; prekursori&nbsp; HAN&nbsp; i hlorpikrina&nbsp; nisu&nbsp; detektovani&nbsp; u&nbsp; sirovoj&nbsp; vodi.&nbsp; Nusproizvodi&nbsp; koji&nbsp; se&nbsp; dominantno&nbsp; formiraju&nbsp; u svim&nbsp; ispitivanim&nbsp; vodenim&nbsp; matriksima&nbsp; su&nbsp; hlorovani&nbsp; THM&nbsp; i&nbsp; HAA,&nbsp; dok&nbsp; se&nbsp; bromovani&nbsp; DBPformiraju u znatno nižim koncentracijama. Zastupljenost bromovanih DBP u temerinskoj vodi<br />je&nbsp; znatno&nbsp; veći&nbsp; u&nbsp; poređenju&nbsp; sa&nbsp; vodom&nbsp; iz&nbsp; Kikinde,&nbsp; kao&nbsp; rezultat&nbsp; prisustva&nbsp; veće&nbsp; koncentracije bromida u sirovoj vodi (0,05&plusmn;0,01 mg Br -/l Temerin; 0,03&plusmn;0,01 mg Br<br />-/l Kikinda). Ispitivanjem&nbsp; uticaja&nbsp; oksidacionih&nbsp; procesa&nbsp; (UV&nbsp; fotolize,&nbsp; ozonizacije,&nbsp; oksidacije vodonik-peroksidom)&nbsp; na&nbsp; sadržaj&nbsp; i&nbsp; reaktivnost&nbsp; POM&nbsp; u&nbsp; ispitivanim&nbsp; vodenim&nbsp; matriksima utvrđeno&nbsp; je&nbsp; da&nbsp; tretman&nbsp; vode&nbsp; UV&nbsp; zračenjem&nbsp; i&nbsp; vodonik-peroksidom,&nbsp; kada&nbsp; se&nbsp; primenjuju&nbsp; kao samostalan&nbsp; tretman,&nbsp; ne&nbsp; pokazuju&nbsp; značajnu&nbsp; efikasnost&nbsp; u&nbsp; smanjenju&nbsp; sadržaja&nbsp; POM.Tretman vode&nbsp; ozonom&nbsp; se&nbsp; pokazao&nbsp; kao&nbsp; veoma&nbsp; efikasan&nbsp; u&nbsp; uklanjanju&nbsp; POM&nbsp; i&nbsp; u&nbsp; smanjenju&nbsp; sadržaja prekursora&nbsp; DBP&nbsp; kod&nbsp; svih&nbsp; ispitivanih&nbsp; vodenih&nbsp; matriksa,&nbsp; kao&nbsp; rezultat&nbsp; smanjenja&nbsp; reaktivnosti POM&nbsp; ka&nbsp; formiranju&nbsp; ovih&nbsp; DBP.&nbsp; Smanjenje&nbsp; sadržaja&nbsp; POM&nbsp; u&nbsp; vodi&nbsp; tokom&nbsp; tretmana&nbsp; raste&nbsp; sa povećanjem&nbsp; primenjene&nbsp; doze&nbsp; ozona,&nbsp; pri&nbsp; čemu&nbsp; se&nbsp; najbolji&nbsp; rezultati&nbsp; postižu&nbsp; pri&nbsp; najvećoj primenjenoj&nbsp; dozi&nbsp; od&nbsp; 3,0&nbsp; mg&nbsp; O 3/mg&nbsp; DOC&nbsp; (do&nbsp; 32%&nbsp; DOC,&nbsp; 92%&nbsp; UV254 sintetički&nbsp; matriks;&nbsp; do 17%&nbsp; DOC,&nbsp; 76%&nbsp; UV 254&nbsp; Kikinda;&nbsp; do&nbsp; 15%&nbsp; DOC&nbsp; i&nbsp; 66%&nbsp; UV254&nbsp;&nbsp;&nbsp; Temerin).&nbsp; U&nbsp; sintetičkom matriksu&nbsp; najveće&nbsp; smanjenje&nbsp; PFTHM&nbsp; (za&nbsp; 76%)&nbsp; i&nbsp; PFHAA&nbsp; (za&nbsp; 80%)&nbsp; u&nbsp; odnosu&nbsp; na&nbsp; sadržaj&nbsp; u sirovoj vodi se postiže pri dozi od 1,0&nbsp; mg O<sub>3 </sub>/mg DOC. Najveće smanjenje PFTHM (za 38%)<br />i PFHAA (za 42%) u vodi iz Kikinde postiže se pri dozi od 3,0 mg O <sub>3 </sub>/mg DOC. U vodi iz Temerina najveće smanjenje PFTHM (za&nbsp; 27%) je pri dozi od 3,0 mg O <sub>3</sub> /mg DOC, dok se za smnjenje&nbsp; PFHAA&nbsp; (za&nbsp; 54%)&nbsp; najbolje&nbsp; pokazala&nbsp; doza&nbsp; od&nbsp; 1,0&nbsp; mg&nbsp; O<br />3 /mg&nbsp; DOC.&nbsp; Sadržaj prekursora&nbsp; HK&nbsp; i&nbsp; HAN&nbsp; (temerinska&nbsp; voda)&nbsp; je&nbsp; veoma&nbsp; nizak&nbsp; nakon&nbsp; tretmana.&nbsp; Tretman&nbsp; vode ozonom&nbsp; vodi&nbsp; ka&nbsp; formiranju&nbsp; DBP&nbsp; sa&nbsp; vi&scaron;e&nbsp;&nbsp; supstituisanih&nbsp; atoma&nbsp; broma,&nbsp; dok&nbsp; u&nbsp; vodama&nbsp; sa srednjim sadržajem bromida (50 &micro;g Br -/l) dovodi do formiranja bromata. Kombinacijom&nbsp; ozonizacije&nbsp; sa&nbsp; UV&nbsp; zračenjem&nbsp; se&nbsp; značajno&nbsp; može&nbsp; pospe&scaron;iti&nbsp; efiksnost uklanjanja&nbsp; POM&nbsp; postignuta&nbsp; primenom&nbsp; samostalne&nbsp; ozonizacije.&nbsp; Najveće&nbsp; smanjenje&nbsp; sadržaja POM u&nbsp; sintetičkom matriksu (za 85% DOC, 98% UV254 i 87% SUVA), u vodi iz Kikinde (za<br />23% DOC, 83% UV 254, 77% SUVA), i vodi iz Temerina (za 15% DOC, 80% UV<br />254 i 75% SUVA), u odnosu na vrednosti u netretiranoj vodi postignuto je pri najvećoj primenjenoj dozi od&nbsp; 3,0&nbsp; mg&nbsp; O<sub> 3</sub> /mg&nbsp; DOC&nbsp; i&nbsp; 6000&nbsp; mJ/cm 2 .&nbsp; Efikasnost&nbsp; procesa&nbsp; raste&nbsp; u&nbsp; vodama&nbsp; u&nbsp; kojima preovladavaju&nbsp; POM&nbsp; veće&nbsp; hidrofobnosti.&nbsp; MeĎutim,&nbsp; iako&nbsp; se&nbsp; O<sub> 3</sub> /UV&nbsp; procesom&nbsp; postiže&nbsp; visok stepen&nbsp; smanjenja&nbsp; PFTHM&nbsp; u&nbsp; sintetičkom&nbsp; matriksu&nbsp; se&nbsp; najbolje&nbsp; pokazao&nbsp; tretman&nbsp; ozonom (1,0 mg&nbsp; O3/mg&nbsp; DOC),&nbsp; dok&nbsp; se&nbsp; najveće&nbsp; smanjenje&nbsp; PFHAA&nbsp; (82%)&nbsp; postiže&nbsp; pri&nbsp; dozi&nbsp; ozona&nbsp; od 1,0 mg O<sub>3/</sub>mg DOC i UV zračenja od 6000 mJ/cm <sup>2 .</sup> U vodi iz Kikinde se PFTHM smanjuje za 50% pri dozi od 3,0 mg O <sub>3</sub>/mg DOC i 6000 mJ/cm 2 , dok se u slučaju uklanjanja prekursora<br />HAA&nbsp; ozonizacija&nbsp; pokazala&nbsp; kao&nbsp; superiorniji&nbsp; proces.&nbsp; U&nbsp; vodi&nbsp; iz&nbsp; Temerina&nbsp; se&nbsp; u&nbsp; pogledu uklanjanja&nbsp; prekursora&nbsp; THM&nbsp; i&nbsp; HAA&nbsp; ozonizacija&nbsp; pokazala&nbsp; kao&nbsp; optimalan&nbsp; proces.&nbsp; Visok alkalitet&nbsp; prirodnih&nbsp; voda&nbsp; inhibira&nbsp; radikalski&nbsp; mehanizam&nbsp; u&nbsp; toku&nbsp; AOP&nbsp; i&nbsp; favorizuje&nbsp; oksidaciju POM molekulskim ozonom.&nbsp; Prekursori HK se formiraju u&nbsp; veoma niskim koncentracijama i njihov sadržaj ne varira značajno tokom tretmana. U prirodnim matriksima tokom AOP pri dozi&nbsp; ozona&nbsp; od&nbsp; 3,0 mg&nbsp; O<sub>3</sub> /mg&nbsp; DOC&nbsp; dolazi&nbsp; do&nbsp; formiranja&nbsp; HAN,&nbsp; međutim,&nbsp; nije&nbsp; uočen&nbsp; jasan trend&nbsp; sa&nbsp; povećanjem&nbsp; doze&nbsp; UV&nbsp; zračenja.&nbsp; Tretman&nbsp; doprinosi&nbsp; formiranju&nbsp; bromovanih&nbsp; vrsta THM,&nbsp; dok&nbsp; se&nbsp; tokom&nbsp; AOP&nbsp; pri&nbsp; najvećoj&nbsp; dozi&nbsp; ozona&nbsp; od&nbsp; 3,0 mg&nbsp; O<sub>3</sub> /mg&nbsp; DOC&nbsp; formiraju bromovani HAN.<br />Najveće&nbsp; smanjenje&nbsp; sadržaja&nbsp; POM&nbsp; primenom&nbsp; kombinacije&nbsp; oksidacije&nbsp; sa&nbsp; H <sub>2</sub>O<sub>2</sub><br />i&nbsp; UV zračenja u sintetičkom matriksu (za do 17% DOC, 70% UV 254 ), u vodi iz Kikinde (za do 22% DOC, 53% UV<sub>254</sub>), i vodi iz Temerina (za do 7% DOC, 68% UV<br /><sub>254 </sub>), u odnosu na vrednosti u sirovoj vodi, se postižu pri dozi H <sub>2</sub>O<sub>2</sub> i UV zračenja od 3,0 mg H<sub>2</sub>O<sub>2</sub>/mg DOC i 6000 mJ/cm <sup>2</sup> .<br />Najveće&nbsp; smanjenje&nbsp; PFTHM&nbsp; od&nbsp; 54%&nbsp; u&nbsp; sintetičkom&nbsp; matriksu&nbsp; se&nbsp; postiže&nbsp; pri&nbsp; dozi&nbsp; od 0 mg H<sub>2</sub>O<sub>2</sub>/mg DOC i 6000 mJ/cm <sup>2</sup> ,&nbsp; dok se smanjenje PFHAA (za 35%)&nbsp; postiže primenom doze vodonik-peroksida i UV zračenja od 1,0 mg H <sub>2</sub>O<sub>2</sub> /mg&nbsp; DOC i 3000 mJ/cm <sup>2</sup> . U vodi izKikinde&nbsp; H<sub>2</sub>O<sub>2</sub> /UV&nbsp; proces&nbsp; ne&nbsp; utiče&nbsp; značajno&nbsp; na&nbsp; sadržaj&nbsp; prekursora&nbsp; THM,&nbsp; dok&nbsp; se&nbsp; najveće smanjenje&nbsp; PFHAA&nbsp; (za&nbsp; 35%)&nbsp; postiže&nbsp; pri&nbsp; dozi&nbsp; od&nbsp; 3,0&nbsp; mg&nbsp; H<sub> <span id="cke_bm_235S" style="display: none;">&nbsp;</span>2<span id="cke_bm_235E" style="display: none;">&nbsp;</span></sub>O<sub>2</sub>/mg&nbsp; DOC&nbsp; i&nbsp; 600&nbsp; mJ/cm <sup>2</sup> .H<span id="cke_bm_184S" style="display: none;">&nbsp;</span><sub>2</sub><span id="cke_bm_184E" style="display: none;">&nbsp;</span>O<sub>2</sub><span id="cke_bm_185E" style="display: none;">&nbsp;</span>/UV&nbsp; proces&nbsp; dovodi&nbsp; do&nbsp; smanjenja&nbsp; PFTHM&nbsp; u&nbsp; Temerinskoj&nbsp; vodi&nbsp; za&nbsp; 74%&nbsp; pri&nbsp; dozi&nbsp; od 3,0 mg H<sub>2</sub>O<sub>2</sub>/mg DOC i 600 mJ/c<span id="cke_bm_236E" style="display: none;">&nbsp;</span>m <sup>2</sup> ,&nbsp; dok primenjeni tretman ne pokazuje značajan uticaj na<br />PFHAA.&nbsp; Prekursori HK su detektovani u sintetičkom matriksu i temerinskoj vodi u niskim koncentracijama.&nbsp; U&nbsp; temerinskoj&nbsp; vodi&nbsp; nakon&nbsp; AOP&nbsp; pri&nbsp; dozi&nbsp; vodonik-peroksida&nbsp; od 3,0 mg H<sub>2</sub>O<sub>2</sub> /mg DOC dolazi&nbsp; do formiranja HAN i hlorpikrina. Primenjeni tretman vodi ka formiranju bromovanih DBP. Svi rezultati dobijeni u toku istraživanja ukazuju na neophodnost optimizacije procesa u&nbsp; tretmanu&nbsp; ispitivanih&nbsp; vodenih&nbsp; matriksa&nbsp; i&nbsp; određivanja&nbsp; optimalnog&nbsp; procesa uzimajući&nbsp; u&nbsp; obzir<br />karakteristika&nbsp; sirove&nbsp; vode&nbsp; i&nbsp; efikasnost&nbsp; koja&nbsp; se&nbsp; želi&nbsp; postići.Kombinacijom&nbsp; dva&nbsp; i&nbsp; vi&scaron;e konvencionalnih&nbsp; tretmana&nbsp; i&nbsp; optimizacijom&nbsp; reakcionih&nbsp; uslova&nbsp; može&nbsp; se&nbsp; postići&nbsp; visoka efikasnost uklanjanja POM, kao i ciljano uklanjanje prekursorskog materijala odabranih DBP, međutim&nbsp; tretman&nbsp; vode&nbsp; ozonom&nbsp; pri&nbsp; dozi&nbsp; od&nbsp; 1,0 mg&nbsp; O<sub>3</sub><br />/mg&nbsp; DOC&nbsp; se&nbsp; pokazao&nbsp; kao&nbsp; optimalan proces.</p> / <p>The aim of the research&nbsp; of&nbsp; this&nbsp; PhD thesis&nbsp; was&nbsp; to determine the effects of various oxidation processes based on ozone, hydrogen peroxide and UV irradiation on the content and reactivity of natural organic matter&nbsp; (NOM)&nbsp; in different water matrices. The&nbsp; tests were carried out&nbsp; on&nbsp; a)&nbsp; groundwater&nbsp; from&nbsp; the&nbsp; territory&nbsp; of&nbsp; Kikinda&nbsp; and&nbsp; Temerin&nbsp; (natural&nbsp; matrix)&nbsp; and&nbsp; b) synthetic aqueous matrix (solution of commercially available humic&nbsp; acid), which differ in the composition&nbsp; and&nbsp; structure&nbsp; of&nbsp; NOM&nbsp; present&nbsp; and&nbsp; the&nbsp; content&nbsp; of&nbsp; bromide.&nbsp; For&nbsp; the&nbsp; oxidation process&nbsp; (ozonation,&nbsp; UV&nbsp; photolysis,&nbsp; oxidation&nbsp; with&nbsp; H 2O2 ,&nbsp; combined&nbsp; O 3 /UV&nbsp; process&nbsp; and combined&nbsp; H 2O2 /UV&nbsp; process),&nbsp; the&nbsp; influence&nbsp; of&nbsp; different&nbsp; doses&nbsp; of&nbsp; oxidants&nbsp; and&nbsp; reaction conditions&nbsp; was&nbsp; examined&nbsp; individually.&nbsp; Particular&nbsp; attention&nbsp; was&nbsp; paid&nbsp; to&nbsp; the&nbsp; influence&nbsp; of&nbsp; the above treatment on the formation of inorganic bromate, as well as the effect on the content of precursors of disinfectant by-products after chlorination (THM, HAA, HAN, HK and CP).Analysis&nbsp; of&nbsp; the&nbsp; chemical&nbsp; parameters&nbsp; of&nbsp; the&nbsp; synthetic&nbsp; matrix&nbsp; (5.44&plusmn;0.30&nbsp; mg&nbsp; C/L; 0.255&plusmn;0.015 cm -1 ;&nbsp; 4.68&plusmn;0.41&nbsp; lm -1 mg -1 )&nbsp; shows&nbsp; that&nbsp; the&nbsp; high-hydrophobic&nbsp; humic&nbsp; compounds predominate in this water. Also, high NOM content of predominantly hydrophobic character was recorded in Kikinda water (5.170.72 mg C/L; 0.2010.001 cm -1 ;&nbsp; 3.88&plusmn;0.70 lm -1 mg -1 ), while&nbsp; NOM&nbsp; content&nbsp; in&nbsp; raw&nbsp; water&nbsp; from&nbsp; Temerin&nbsp; (2.060.38&nbsp; mg&nbsp; C/L;&nbsp; 0.0500.001&nbsp; cm -1 ; 2.43&plusmn;0.21 lm -1 mg -1 ) significantly lower and predominate NOM of hydrophilic character. A higher degree of hydrophobicity of the synthetic matrix in comparison with&nbsp; natural matrices, resulted in higher reactivity of organic matter with chlorine, which can be concluded on&nbsp; the&nbsp; basis&nbsp; of&nbsp; high&nbsp; PFDBP&nbsp; values&nbsp; after&nbsp; chlorination.&nbsp; The&nbsp; PFTHM&nbsp; value&nbsp; in&nbsp; the&nbsp; synthetic matrix&nbsp; was&nbsp; 544&plusmn;85.9 &micro;g/L, while the PFTHM in the raw waters from Kikinda and Temerin was&nbsp; significantly&nbsp; lower&nbsp; (279&plusmn;32.3&nbsp; and&nbsp; 180&plusmn;44.0&nbsp; &micro;g/L,&nbsp; respectively).&nbsp; The&nbsp; PFHAA&nbsp; value&nbsp; in the&nbsp; synthetic&nbsp; matrix&nbsp; was&nbsp; 484&plusmn;77.5&nbsp; &micro;g/L,&nbsp; while&nbsp; PFHAA&nbsp; in&nbsp; the&nbsp; Kikinda&nbsp; water&nbsp; was 223 244&plusmn;11.1 &micro;g/L&nbsp; and in&nbsp; the&nbsp; Temerin&nbsp; water&nbsp; was&nbsp; 165&plusmn;32.5 &micro;g/L.&nbsp; The content of&nbsp; precursors of HK&nbsp; (8.05&plusmn;3.63&nbsp; &micro;g/L&nbsp; synthetic&nbsp; matrix;&nbsp; 14.91.38&nbsp; &micro;g/L&nbsp; Kikinda;&nbsp; 7.400.25&nbsp; &micro;g/L&nbsp; Temerin) was&nbsp; significantly&nbsp; lower&nbsp; compared&nbsp; to&nbsp; precursors&nbsp; of&nbsp; THMs&nbsp; and&nbsp; HAAs,&nbsp; while&nbsp; precursors&nbsp; of HANs&nbsp; and&nbsp; chloropicrin&nbsp; were&nbsp; not&nbsp; detected&nbsp; in&nbsp; raw&nbsp; water.&nbsp; The&nbsp; by- products&nbsp; that&nbsp; were predominantly&nbsp; formed&nbsp; in&nbsp; all&nbsp; the&nbsp; tested&nbsp; water&nbsp; matrices&nbsp; were&nbsp; chlorinated&nbsp; THMs&nbsp; and&nbsp; HAAs, while the brominated DBPs&nbsp; were&nbsp; formed at substantially lower concentrations. The presence of&nbsp; brominated DBPs&nbsp; in&nbsp; Temerine&nbsp; water&nbsp; were&nbsp; significantly higher compared to Kikinda water as&nbsp; a&nbsp; result&nbsp; of&nbsp; the&nbsp; presence&nbsp; of&nbsp; higher&nbsp; bromide&nbsp; content&nbsp; in&nbsp; raw&nbsp; water&nbsp; (0.05&plusmn;0.01&nbsp; mg&nbsp; Br -/L Temerin; 0.03&plusmn;0.01 mg Br -/L Kikinda). By&nbsp; examining&nbsp; the&nbsp; influence&nbsp; of&nbsp; oxidation&nbsp; processes&nbsp; (UV&nbsp; photolysis,&nbsp; ozonation,hydrogen&nbsp; peroxide&nbsp; oxidation)&nbsp; on&nbsp; the&nbsp; content&nbsp; and&nbsp; reactivity&nbsp; of&nbsp; NOM&nbsp; in&nbsp; the&nbsp; tested&nbsp; water matrix, it was&nbsp; found that the UV&nbsp; irradiation and&nbsp; treatment by&nbsp; hydrogen peroxide, when used as an independent treatment, did&nbsp; not show significant efficacy in reducing the&nbsp; NOM content. Water treatment by ozone&nbsp; proved to be very effective in eliminating&nbsp; NOM and reducing the content of DBP precursors in all tested water&nbsp; matrices, as a result of the reduction of&nbsp; NOM reactivity &nbsp; to&nbsp; the&nbsp; formation&nbsp; of&nbsp; these&nbsp; DBPs.&nbsp; Reduction&nbsp; of&nbsp; NOM&nbsp; content&nbsp; in&nbsp; water&nbsp; during treatment increased&nbsp; with increasing the applied dose of ozone, with the best results achieved at the highest dosage of&nbsp; 3.0 mg O 3/mg DOC&nbsp; (up to 32% DOC, 92% UV 254&nbsp; synthetic matrix, up&nbsp; to&nbsp; 17%&nbsp; DOC,&nbsp; 76%&nbsp; UV 254 Kikinda,&nbsp; up&nbsp; to&nbsp; 15%&nbsp; DOC&nbsp; and&nbsp; 66%&nbsp; UV254 Temerin).&nbsp; In&nbsp; the synthetic&nbsp; matrix the highest reduction&nbsp; in&nbsp; PFTHM (76%) and PFHAA (by 80%)&nbsp; compared to raw water content&nbsp; was&nbsp; achieved at a dosage&nbsp; of 1.0 mg O 3/mg DOC. The highest reduction in PFTHM&nbsp; (38%)&nbsp; and&nbsp; PFHAA&nbsp; (42%)&nbsp; in&nbsp; Kikinda&nbsp; water&nbsp; was&nbsp; achieved&nbsp; at&nbsp; a&nbsp; dose&nbsp; of 3.0 mg O3 /mg DOC. In Temerin water, the highest reduction in PFTHM (27%) was at a dose of&nbsp; 3.0 mg O 3/mg DOC, while the dose of 1.0&nbsp; mg O3 /mg&nbsp; DOC&nbsp; was best shown for removing PFHAA (by 54%). The content of the precursors of HKs and HANs (Temerin water) was very low&nbsp; after&nbsp; treatment.&nbsp; Water&nbsp; treatment&nbsp; by&nbsp; ozone&nbsp; led&nbsp; to&nbsp; the&nbsp; formation&nbsp; of&nbsp; DBPs&nbsp; with&nbsp; more substituted bromine atoms, while in waters with a mean bromide content (50 &mu;g Br -/L) led&nbsp; to bromate formation.Combination of ozonation with UV irradiation can greatly accelerate the effectiveness of&nbsp; NOM&nbsp; removal&nbsp; achieved&nbsp; by&nbsp; the&nbsp; use&nbsp; of&nbsp; ozonation&nbsp; alone.&nbsp; The&nbsp; highest&nbsp; reduction&nbsp; in&nbsp; NOM content in the synthetic matrix (by 85% DOC, 98% UV 254 and 87% SUVA), in Kikinda water (by 23%&nbsp; DOC, 83% UV 254 , 77% SUVA) and water from Temerin (by 15% DOC, 80% UV 254 and 75% SUVA), compared to the values in&nbsp; raw&nbsp; water, was achieved at the highest&nbsp; dose of 3.0&nbsp; mg&nbsp; O 3 /mg&nbsp; DOC&nbsp; and&nbsp; 6000&nbsp; mJ/cm 2 .&nbsp; The&nbsp; efficiency&nbsp; of&nbsp; the&nbsp; process&nbsp; was&nbsp; growing&nbsp; in&nbsp; the waters where NOM predominates of hydrophobicity. Although the O 3 /UV process achieved a high&nbsp; degree&nbsp; of&nbsp; reduction&nbsp; in&nbsp; PFTHM&nbsp; in&nbsp; the&nbsp; synthetic&nbsp; matrix&nbsp; the&nbsp; ozonation (1.0 mg O3 /mg DOC)&nbsp; was&nbsp; proved&nbsp; as&nbsp; more&nbsp; efficient,&nbsp; while&nbsp; the&nbsp; highest&nbsp; reduction&nbsp; in&nbsp; PFHAA (82%)&nbsp; was&nbsp; achieved&nbsp; at&nbsp; a&nbsp; ozone&nbsp; dose&nbsp; of&nbsp; 1.0&nbsp; mg&nbsp; O 3/mg&nbsp; DOC&nbsp; and&nbsp; UV&nbsp; irradiation&nbsp; of 6000 mJ/cm 2 . In the water from Temerin,&nbsp; in case to removal of precursors of THM and HAA, ozonation&nbsp; was proved&nbsp; to be an optimal process. High alkalinity of natural waters&nbsp; inhibits the radical &nbsp; mechanism&nbsp; during&nbsp; AOP&nbsp; and&nbsp; favors&nbsp; NOM&nbsp; oxidation&nbsp; with&nbsp; molecular&nbsp; ozone.&nbsp; HKs precursors were formed at very low concentrations and their content did not vary significantly during&nbsp; the&nbsp; treatment.&nbsp; In&nbsp; natural&nbsp; matrices&nbsp; during&nbsp; the&nbsp; AOP&nbsp; at&nbsp; a&nbsp; ozone&nbsp;&nbsp; dose&nbsp; of 3.0 mg O3 /mgDOC, HANs&nbsp; were&nbsp; formed, however, there&nbsp; was&nbsp; no clear trend with increasing UV irradiation. The treatment contributed to the formation of brominated THM species, while during&nbsp; the&nbsp; AOPs,&nbsp; brominated&nbsp; HANs&nbsp; were&nbsp; formed&nbsp; at&nbsp; the&nbsp; maximum&nbsp; dose&nbsp; of&nbsp; ozone&nbsp; of 3.0 mg O3/mg DOC. 224 The largest decrease in&nbsp; NOM content by the combination of oxidation with H2O2 and UV irradiation in the synthetic matrix (for up to 17% DOC, 70% UV 254 ), in Kikinda water (up to 22% DOC, 53% UV 254), and water from Temerin&nbsp; (7% DOC, 68% UV 254 ), compared&nbsp; to the values&nbsp; in&nbsp; raw&nbsp; water,&nbsp; were&nbsp; obtained&nbsp; at&nbsp; a&nbsp; dose&nbsp; of&nbsp; H 2O2 and&nbsp; UV&nbsp; irradiation&nbsp; of 3.0 mg O3 /mg DOC&nbsp; and 6000 mJ/cm 2 . The highest PFTHM reduction of 54% in the&nbsp; synthetic matrix was achieved at a dosage of 1.0 mg H2O2/mg DOC and 6000 mJ/cm 2 , while a decrease in&nbsp; PFHAA&nbsp; (35%)&nbsp; was&nbsp; achieved&nbsp; using&nbsp; a&nbsp; dose&nbsp; of&nbsp; hydrogen&nbsp; peroxide&nbsp; and&nbsp; UV&nbsp; irradiation&nbsp; of 1.0 mg H2O2/mg DOC and 3000 mJ/cm 2 . In the water from Kikinda, the H2O2 /UV process did not significantly affect on the THM precursors content, while the highest reduction in PFHAA (35%)&nbsp; was&nbsp; achieved&nbsp; at&nbsp; a&nbsp; dose&nbsp; of&nbsp; 3.0&nbsp; mg&nbsp; H2O2/mg&nbsp; DOC&nbsp; and&nbsp; 600&nbsp; mJ/cm 2 .&nbsp; The&nbsp; H 2O2 /UV process&nbsp; led&nbsp; to&nbsp; a&nbsp; decrease&nbsp; in&nbsp; PFTHM&nbsp; in&nbsp; the&nbsp; Temerin&nbsp; water&nbsp; by&nbsp; 74%&nbsp; at&nbsp; a&nbsp; dose&nbsp; of 3.0 mg&nbsp; 2O2 /mg&nbsp; DOC&nbsp; and&nbsp; 600&nbsp; mJ/cm 2 ,&nbsp; whereas&nbsp; the&nbsp; treatment&nbsp; applied&nbsp; had&nbsp; no&nbsp; significant effect on PFHAA. HKs precursors were detected in synthetic matrix and the Temerin water at low&nbsp; concentrations.&nbsp; In&nbsp; the&nbsp; water&nbsp; after&nbsp; the&nbsp; AOP&nbsp; at&nbsp; a&nbsp; dose&nbsp; of&nbsp; 3.0&nbsp; mg&nbsp; H 2O2 /mg&nbsp; DOC&nbsp; of hydrogen&nbsp; peroxide,&nbsp; HANs&nbsp; and&nbsp; chloropicrin&nbsp; were&nbsp; formed.&nbsp; The&nbsp; applied&nbsp; treatment&nbsp; led&nbsp; to&nbsp; the formation of brominated DBPs.<br />All the results obtained during the research indicate the necessity of optimization&nbsp; the process&nbsp; in&nbsp; the&nbsp; treatment&nbsp; of&nbsp; the&nbsp; examined&nbsp; water&nbsp; matrices&nbsp; and&nbsp; determination&nbsp; of&nbsp; the&nbsp; optimal process taking into account the characteristics of&nbsp; raw water and the efficiency to be achieved. By combining two or more conventional treatments and optimizing the reaction conditions, high&nbsp; NOM removal efficiency can be achieved, as well as removal of the&nbsp; targeted&nbsp; precursor material&nbsp; of&nbsp; the&nbsp; selected&nbsp; DBPs,&nbsp; but&nbsp; the&nbsp; treatment&nbsp; of&nbsp; ozone&nbsp; water&nbsp; at&nbsp; a&nbsp; dose&nbsp; of 1.0 mg O3 /mg DOC was proved to be an optimal process.</p>

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