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UV Advanced Oxidation for Treatment of Taste and Odor and Algal Toxins

UV Advanced Oxidation for Treatment of Taste and Odor and Algal Toxins. Ohio AWWA Annual Conference Research Workshop September 20, 2011 Erik Rosenfeldt, PE, PhD. Presentation Agenda. Algae issues Taste and Odor Toxic Substances Climate change impacts on algae events

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UV Advanced Oxidation for Treatment of Taste and Odor and Algal Toxins

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  1. UV Advanced Oxidation for Treatment of Taste and Odor and Algal Toxins Ohio AWWA Annual Conference Research Workshop September 20, 2011 Erik Rosenfeldt, PE, PhD

  2. Presentation Agenda • Algae issues • Taste and Odor • Toxic Substances • Climate change impacts on algae events • UV Advanced Oxidation • Fundamentals • Treatment of taste and odor, toxins • Comparisons with other technologies • Summary and Conclusions

  3. Algae Issues • Seasonal algae blooms present many problems for water utilities • Depleted oxygen • Turbidity • Taste and Odor • Cyanobacteria • “Blue-green” algae • Not quite algae, not quite bacteria • Photosynthetic but lack well-defined nucleus • Responsible for Taste and Odor compounds • Create and may release toxic compounds

  4. Algal Taste and Odor Compounds • Methylisoborneol (MIB) and geosmin • Musty/earthy odor detectable at low (5-10 ng/L levels) • Non-toxic • Released by cyanobacteria • Not regulated, but public perception rules

  5. Cyanotoxins • Some blue-green can produce one or more toxins • Do not produce toxins at all times • Toxins can affect • Fish and other aquatic life • Livestock • Pets • Humans • Exposure routes in humans • Dermal • Oral (water or food) • Inhalation • Dialysis • Included on US EPAs CCL3

  6. Cyanotoxins Tedesco et al, 2011

  7. Cyanotoxin Occurrence Indiana data • Yearly occurrence • Occurs during algal blooms • Late summer, early fall • Toxins typically released during lysis • Algae mitigation processes can make problem worse Tedesco et al, 2011

  8. Cyanotoxins in Ohio • Lake Erie and Grand Lake St. Marys Algal Blooms • Last year: Ohio EPA testing revealed 0.23 and 0.16 ppb Microcystin in two treated drinking waters • Lake Erie Source: • Potassium Permanganate, PAC, Lime Softening, Filtration, Chlorine • Lake Erie Source: • Raw water filtration, Ozone, adsorption clarifier, chlorine disinfection

  9. Cyanotoxins and Taste and Odor • USGS 2010 study (ES&T 44, 7361 – 7368) • Sampled 23 Midwest lakes • Multiple toxin classes co-occurred in 48% • Toxins and T&O co-occurred in 91% • No health risks during T&O outbreaks?

  10. Climate Impacts on Algae • Temperature • Warmer temperatures encourage blooms (Pearl and Huisman, 2008) • Warmer temperatures increase the odor intensity of VOCs at very low concentrations, increasing consumer detection (Whelton et al., 2004) • Precipitation • Long antecedent dry periods increase nutrient content of runoff • Low rainfall can cause stagnant conditions in the watershed • Wind/storms • Heavy storms and strong wind can mix reservoirs, reintroducing nutrients into the water column from bottom sediments

  11. Northeast Climate Projections • Temperature • 3° to 7°C temperature increase by 2100 (Frumhoff et al, 2007) • More frequent days over 35°C (Karl et al, 2009) • Precipitation • 5 to 10% increase, mostly in fall and winter (Frumhoff et al, 2007) • Storms • Increasing trends in extreme precipitation (Spierre and Wake, 2010)

  12. What will OH’s climate look like? Lower Emissions Scenario Higher Emissions Scenario 2010 - 2039 2010 - 2039 2040 - 2069 2070 - 2090 2040 - 2069 2070 - 2090 Adapted from Frumhoff et al, 2007

  13. What can be done? • Algae blooms are getting more prevalent and potentially more dangerous • Fortunately, algae typically only occur in the summer months • Several treatment processes are effective • Activated Carbon • GAC • PAC • Ozone • UV Advanced Oxidation (UV AOP)

  14. Advanced Oxidation Processes • An effective process for disinfection and chemical oxidation, capable of providing barriers for protecting public health and improving public perception • Pharmaceuticals, Personal Care Products, EDCs • Crypto, Viruses, E. coli, etc. • AOPs work by creating hydroxyl radicals (•OH) • •OH then blast away at organic chemicals • Usually an expensive chemical process • Complex chemistry • UV Based AOPs • UV/H2O2, UV/O3, UV/HOCl, etc. • Ozone Based AOPs • Ozone/H2O2, Ozone/NOM, Ozone/pH

  15. Org Org H2O H2O H2O2 H2O2 H2O2 • OH • OH • OH • OH UV/H2O2 AOP • H2O2 absorbs UV energy and degrades to 2 OH radicals • Only 1 OH radical per UV photon • Due to “water caging” UV Absorbance of H2O2

  16. 16 Fundamentals – UV/H2O2 AOP • AOP  High powered oxidation of contaminants via OH radical intermediate • OH radical is very reactive with “targets” • OH radical is also reactive with “scavengers”

  17. Differences between UV disinfection and AOP • Some fundamental differences in • Levels of Applied UV Energy • Fundamental Mechanisms • UV Dose (ie what does it mean?) • Different “Targets” Disinfection Photolysis AOP

  18. UV AOP for Taste and Odor UV Advanced Oxidation UV Photolysis Rosenfeldt and Linden, 2005 UV Advanced Oxidation for Geosmin Oxidation at Cornwall, ON TrojanUV, 2010

  19. UV AOP for Algal Toxins UV and UV AOP for m-LR destruction UV AOP for MIB and algal toxins at Cornwall, ON Alvarez et al, 2010 Approximate Geosmin removal UV and UV AOP for m-RR destruction TrojanUV, 2010 Qiao et al, 2005

  20. Taste and Odor as a surrogate for toxin oxidation? • Characteristics of a good surrogate • Co-occurrence (Graham et al, 2010) • Microcystin co-occurred with geosmin in 87% of blooms, with MIB in 39%. • Anatoxin-a co-occurred with geosmin in 100% of blooms, with MIB in 43%. • Similar trends of occurrence (Graham et al, 2010) • Although toxins and T&O frequently co-occurred, concentrations were not strongly correlated (r < 0.4, p > 0.1) • Not surprising because they are not produced by the same biochemical pathways • Surrogate is conservative • Microcystin LR and Anatoxin degraded faster than MIB, but not geosmin

  21. Why UV AOP makes some sense • “Instant-on” technology • Effective Disinfection / Innovative Technology • Comparable replacement for other T&O treatment processes Pantin, 2009

  22. Why UV AOP makes some sense Cornwall, ON • Trojan UV SwiftTMECT Reactors (MP technology) • UV system serves in disinfection mode” most of the year (4 of 8 lamps running) • Can “ramp-up” to AOP conditions seasonally (8 lamps running, add H2O2) • 5 operational levels  UV dose ~ 400 – 60 mJ/cm2 • H2O2 varies 1, 2, 4, 8, 15 mg/L UV AOP replaces GAC filter caps for T&O control ($100,000/yr for GAC replacement). UV provides excellent disinfection barrier Pantin, 2009

  23. Why UV AOP makes some sense Neshaminy Water Treatment Plant • Civardi and Lucca, 2010 (OAWWA and Tricon) compared costs and carbon footprint for 20 year design life • 15 MGD Plant, Desired 1 log removal of “Geosmin and MIB” • Assume 90 days per year of use (each is “instant-on”) Civardi and Lucca, 2010

  24. Why UV AOP makes some sense • Byproducts? • In most cases, this is a major impact on AOP feasibility • Eg: Estrogenic activity of BPA goes away slower than BPA BPA

  25. Byproducts • In the case of UV AOP treatment of taste and odor and toxins, the story is simpler… • Taste and odor and toxic action are very dependent on molecular structure • Small changes in structure (ie oxidation, phototransformation, etc.) will likely diminish toxicity significantly Anatoxin-a 250 mg/kg Anatoxin-a(S) 20 mg/kg MIB No toxicity

  26. Wrap Up • Algal toxins and algae related taste and odor outbreaks are both caused by seasonal, cyanobacteria outbreaks • Recent research has indicated that presence of taste and odor (geosmin particularly), correlates well with presence of algal toxins • UV Advanced Oxidation effectively degrades both T&O and algal toxins • In general, MIB < Geosmin ~ Anatoxin << Microcystin • Cost and carbon footprint similar to Activated Carbon • “Instant-on” Technology

  27. Parting thought… “Drinking water purveyors frequently tell customers during taste-and-odor outbreaks that there are no health risks. In our study, however, taste-and-odor causing compounds were always accompanied by cyanotoxins, highlighting the need for water purveyors to increase cyanotoxin surveillance during taste-and-odor outbreaks so that treatment can be modified accordingly, and to verify that cyanotoxins are not present at or above thresholds of potential health risk.” Graham et al, 2010

  28. Questions? Erik Rosenfeldt, P.E., PhD Hazen & Sawyer Fairfax 703-537-7920 571-505-6601 erosenfeldt@hazenandsawyer.com

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