Why Use ClO2 For Drinking Water Treatment? Ron Hofmann Department of Civil Engineering, University of Toronto Osvaldo Conio, Fiorina De Novellis Fondazione AMGA ClO2 usage North America (1o) Primary disinfection and oxidation Secondary (2o) disinfection Surface waters 3% Ground waters 0.2% Italy 20% < 1% United States Environmental Protection Agency (2002) Meucci, L., and O. Conio (1996). First European Symposium on chlorine dioxide and disinfection. Why use ClO2? DISINFECTION Primary (1o) disinfection Secondary (2o) disinfection TASTE AND ODOURS DISINFECTION BY-PRODUCTS IMPROVE DOWNSTREAM TREATMENT IRON/MANGANESE DESTRUCTION OF ORGANIC POLLUTANTS Disinfection 1o and 2o disinfection Primary: making the water safe before it leaves the treatment plant (before the first person drinks the water) Secondary: protecting the water as it travels to the home Coag/flocc Settling Filter Clearwell Water Treatment Plant ClO2 for 1o disinfection ClO2 is a powerful disinfectant (usually much stronger than chlorine, not as strong as ozone) Disinfectant doses in North America controlled by CT requirements CT requirements can be used to compare disinfectant strengths (ClO2 vs. Cl2 vs. O3) No Note : log = kCT N where N is number of surviving organisms Number of organisms CT CT requirements If 20oC, and need 2-log Giardia reduction: need CT = 10.0 mg⋅min/L If 30 minutes available before the first customer → ClO2 = 10 mg ⋅ min/L = 0.33 mg/L 30 min CT For 2-log VIRUS Inactivation (10oC) 12 643 CT (mg min/L) 10 8 Cl2 and ClO2 are similar for viruses 6 4 2 0 Cl2 ClO2 NH2Cl O3 CT For 2-log GIARDIA Inactivation (10oC) 120 1230 100 CT (mg min/L) ClO2 is about 5X stronger than Cl2 for Giardia 80 60 40 20 0 Cl2 ClO2 NH2Cl O3 CT For 2-log CRYPTO Inactivation (10oC) 1000 900 ?? > 15,000? CT (mg min/L) 800 700 ClO2 will get some Crypto kill 600 500 400 300 200 100 0 Cl2 ClO2 NH2Cl O3 ClO2 for 1o disinfection If Cryptosporidium disinfection not required: ClO2 doses and/or times can be much lower than Cl2 for Giardia & virus control ClO2 often a good replacement for Cl2 when contact time (= volume) is limited In practice in North America: ClO2 not a common 1o disinfectant. UV, O3 normally used when Cl2 not possible ClO2 for 2o disinfection In Europe - fairly common. Reasons: No regulation to maintain a residual at the tap (often undesirable) Note: ClO2 usually less stable than Cl2 Good multipurpose disinfectant/oxidant In North America - almost never used. Reasons: Less stable – can’t maintain residual at the tap Difficulty with analytical method in the field Taste and odour problems Disinfection summary In Europe ClO2 can be used alone since no need for 2o disinfectant attractive choice in some cases In North America ClO2 cannot be used alone → makes ClO2 less popular Secondary disinfectant Preferred 1o Less popular Cl2 NH2Cl Cl2, UV O3, ClO2 Taste and odour control Historically the most common ClO2 application Experience: ClO2 destroyed T&O problems that Cl2 or KMnO4 could not Research: ClO2 not very effective for geosmin, 2-methylisoborneol (MIB), common pyrazines and anisoles Research: ClO2 effective for sulfides, phenolics Conclusion: ClO2 controls T&O in some waters, but need research to identify the specific compounds Disinfection By-Products (DBPs) Trihalomethanes Haloacetic Acids Chlorite Chlorate North America 0.080 mg/L 0.060 mg/L 1 mg/L None Europe 0.025-0.150 mg/L None 0.2-0.7 mg/L 0.7 mg/L Pure ClO2 forms no THMs; very low HAAs Pure ClO2 followed by NH2Cl (2o disinfectant) effective Chlorite (ClO2-) and chlorate (ClO3-) are a concern About 70% of applied ClO2 ends up as chlorite when reacting with natural organic matter 5 Chlorite (mg/L) Korn et al. 1998 8 waters, different pH, temperatures y = 0.6968x - 0.0487 2 R = 0.9518 4 3 2 y = 0.6815x R2 = 0.951 1 0 Chlorite = 70% of reacted ClO2 0 1 2 3 4 5 6 Chlorine Dioxide consumed (mg/L) Chlorate (mg/L) 0.6 Chlorate = 9% of reacted ClO2 y = 0.0906x - 0.0008 2 R = 0.8537 0.5 0.4 0.3 y = 0.0904x 2 R = 0.8537 0.2 0.1 0 0 1 2 3 4 5 Chlorine Dioxide consumed (mg/L) 6 ClO2 as a preoxidant: sometimes lower Cl2 THMs/HAAs ClO2 Cl2 Coag/flocc Settling Filter Clearwell 160 Total THMs (μg/L) 140 No pretreatment 1 mg/L ClO2 pretreatment Often an easy change to make Less effective for HAAs than for THMs Does ClO2 affect treatment? 120 100 80 60 40 20 0 Waterloo, ON NY State #1 NY State #2 ClO2: impact on downstream treatment Very little reported information; a lot of “stories” ClO2 preoxidation make filters run longer ClO2 preoxidation improves coagulation Change Cl2 proxidation to ClO2, with Cl2 applied after filters Result: turbidity formed after filters. Why? Possible reducing conditions in filter releases Fe2+, then Cl2 + Fe2+ → Fe3+ precipitate AwwaRF 2005: pilot-scale tests of ClO2 preoxidation settled water turbidity, total organic carbon, UV254nm filtered turbidity, particle counts, headloss, organic carbon Example: settled water turbidity 3.00 Turbidity (NTU) 2.50 2.00 Raw Water No ClO2 ClO2 1 mg/L ClO2 0.6 mg/L ClO2 1.50 1.00 0.50 0.00 17-Aug 6-Sep 26-Sep 16-Oct Sampling Dates 5-Nov No statistically significant impact of ClO2 on settling tank or filter performance for 1 water tested in California. Fe/Mn control Fe is easy to oxidize (air, Cl2, ClO2…) Cl2 does not quickly oxidize Mn (KMnO4 often used – but does not disinfect) ClO2 oxidizes Mn within seconds serves to disinfect at the same time reportedly unaffected by normal pH range Fe/Mn control Manganese stoichiometry: 2.45 mg ClO2 per mg Mn(II) → ClO2 reduced to ClO2- (not Cl-) Natural organic matter interferes: Competes for ClO2 reaction Forms Mn-complexes that are resistant to ClO2 Overcome by adding excess ClO2 (e.g. 200%-300%) Limited effectiveness against some Mn-complexes Must do tests to predict ClO2 effectiveness Destruction of organic pollutants Phenolics Rapid oxidation Pesticides Very few studies on oxidation by ClO2: show poor results Endocrine disrupting compounds and pharmaceuticals Limited research; behaves similarly to chlorine No strong reason to use ClO2 for destruction of specific organic pollutants Why use ClO2? ClO2 is a very good disinfectant European disinfection regulations make ClO2 attractive North American disinfection regulations make ClO2 less attractive ClO2 may be best for multiple treatment objectives e.g. disinfection + taste and odour/Fe,Mn Opportunity: learn more about taste and odour control using ClO2 too many “stories”, too little science!
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