Improving TOCs, DBPs, and Chlorine Residuals
Transcription
Improving TOCs, DBPs, and Chlorine Residuals
4/2/2012 Improving TOCs, DBPs, and Chlorine Residuals Mike Ricks April 17, 2012 • Filter Media Effectiveness • Problems of less Efficient Media • Options • Problems with Organics / Algae • Treatments 1 4/2/2012 • Trouble with short Filter runs • Trouble with Clogged Under drains • Trouble with mixing of my media layers • Trouble with Media “Growth” • Trouble with Channeling, “Mudballs”, and cementing • Trouble with increase in turbidity & High Head loss • Trouble with iron still coming through the filter • Trouble with too little time and money What we all Want To go from This To This 2 4/2/2012 Fe/Mn Mn Mn/Fe Mn/CaCO3 Clean CaCO3 Cake CaCO3/Fe Iron Bacteria CaCO3 3 4/2/2012 Media Density 120 Before Aftfer 100 102 100 Nominal #/ft3 80 60 63 58 52 50 40 20 0 Anthracite Sand Media Distribution Top 12” ” % Volume 80 Sand 60 53 50 72 Anthracite 70 47 40 28 30 20 10 0 Before After 4 4/2/2012 Filter Media Effectiveness Operators Typically Adjust their procedures to compensate for this degradation of their media 100 90 80 70 60 50 Filter Media Effectiveness 40 30 20 10 0 Year 1 Year 2 Year 3 Year 4 Year 5 Year 6 Year 7 Year 8 Year 9 Year 10 Filter Media Effectiveness No Cleaning 100 Shorter Filter Runs Increase Fe & Mn levels Turbidity Breakthrough Uneven Backwash High Starting Head Loss 90 80 70 60 50 40 30 20 10 0 Year 1 Year 2 Year 3 Year 4 Year 5 Year 6 Year 7 Year 8 Year 9 Year 10 5 4/2/2012 Filter Media Effectiveness 100 90 80 70 60 50 Filter Media Effectiveness 40 30 20 10 0 Year 1 Year 2 Year 3 Year 4 Year 5 Year 6 Issues • Bio- Mass Increases the size of media particles • Year 7 Year 8 Year 9 Year 10 Anthracite Get degradation of capacity and filtration properties of media • Reduction in uniformity of media particles • Alters flow and degrades filter performance • Deposits Mask Angularity of the Media • Sharp edges needed to create turbulent flow – deposits take this away by covering edges 6 4/2/2012 Issues Cleaned • Masking of the adsorptive surfaces • Deposits occupy the bonding sites that remove contaminants • Altering of the Density of the media due to build-up • Lose transition zones and don’t settle in proper spots after backwash • Decrease Effective Depth of media • Media “growth” leads media washout during backwash • Get Mudballs, Cementing, & Channeling • U–G–L-Y water channels around clumps and slabs and are not filtered • Block Under drains and Direct Media Support • Result in high head pressure during filtration and high backwash pressures during backwash • Degrades backwash effectiveness and damages under drains • Operators backwash to remove deposits on the media • However, small deposits always remain and build up over time 7 4/2/2012 • Short or Declining Filter run times • High Starting head loss • Turbidity Break through Time to Fix It • Uneven Backwash • High backwash pressures • Loss of media • High pressure can lead a complete Re-Build of the entire Filter • Can See Media Growth • Iron & Manganese levels in finished water • Call your Engineer or Well Driller for Filter Rehabilitation and media replacement • Go to the Town board and ask for a rate increase • Hire more people or re-assign other peoples duties to help with filters • Seek alternatives to replacement 8 4/2/2012 • Drain Filter • Get sample from anthracite and sand • Get multiple samples from different areas of filters • “Z” Pattern WSU Cleaing Filter Information Sheet City / Utility: Treatment Plant: Contact Person: Address: City: Phone - Office E-mail Title: State: Phone -Cell Fax: Zip: Filter Type & other Basics Filter Manufacturer and Model # Gravity & number Pressure Vessel & number Concrete: Steel: Vertical: Horizontal: Package Plant Aerolater Others Location: Indoors: Outdoors: # offiline at once Core Sample taken from Filter # Size: Length (feet) Width: Height: Diameter: Media Depth (inches) Anthracite Sand Greensand Gravel Last Year Media Exchanged: Chemically Cleaned: 9 4/2/2012 • Lab Report is a Must • • • • Not the “Hand Test” 8-10 Page report • Will do a Sieve Analysis Shows what deposits have built up Shows how much can be removed • Which chemical blend is most efficient Shows Expected benefits from a good cleaning • Even if you do Nothing – this is a great thing for your file and decision making progress • Great to show Town Board, Mayor, etc on condition of Filters and when something needs to go into the budget 10 4/2/2012 Low / Acceptable Moderate Significant High Severe Recommended Treatment (per Filter) Will Depend on make-up of mineral deposits Primarily Iron and Manganese and magnesium Blended MC – 444 Primarily lime, hard water scale deposits and calcium Blended MC – 477 Many facilities need a combination Also need CA-500 as a catalyst Often need a neutralizer 11 4/2/2012 Reduced Head Loss Reduced Effluent Turbidity Improved Media Stratification Longer Filter Runs Improved Backwash Flow Reduced Chlorine Demand Removal of Mudballs Prevent/Reverse Cementing Cleaning of Underdrain Extended Media Lifetime Anthracite Untreated x Likely x x x x Anthracite Treated 12 4/2/2012 Sand Untreated Sand Treated Sand Untreated Sand Treated 13 4/2/2012 Green Sand Untreated Green Sand Treated 14 4/2/2012 15 4/2/2012 Before Cleaning/After Cleaning Small Deposits Clean Media The orange and black on the Before picture are the deposits. The black particles in the After picture are the black sand particles. 16 4/2/2012 • “Hide” in under drains • Never go away • In source water • Can be heavier in corners and under drains than in media itself • Can be removed with cleaning 17 4/2/2012 Replacement Clean • $30 - $90 per Cubic Foot • Usually $10-$30 per cubic foot • May take 3-5 days per filter • 1-2 days per filter to clean • Under drains, and filter walls are not cleaned • Will clean Under drains, support gravel, & filter walls • 100% new media • like new media Replaced • $26,500 $48 per cubic foot • New Media and gravel $8,000 including Freight • Labor $17,000 • $1,500 unexpected welding needed Cleaned Filter –Est. • $13,250 to clean $24 per cubic foot • May be cleaned every 2-5 years for $6 9,000 • With cleaning will likely go 20 years + before replacement • Under drains, and filter walls not cleaned 18 4/2/2012 Replacement • Initial Replacement and Replaced every 3-4 years (3% inflation) • Year 1 $26,500 • Year 5 $29,826 • Year 8 $32,592 • Year 12 $36,682 • Year 15 $40,084 • $175,062 Replacement • Initial Replacement and replaced every 7 years (3% inflation) • Year 1 $26,500 • Year 8 $ 32,592 • Year 15 $40,084 • $99,175 Takes you through Year 15 Cleaning – 50% of Replacement • 1st Cleaning and subsequently yearly cleanings (3% inflation) • Year 1 $13,250 • Year 2 $6,824 • Etc. thru Year 15 $10,021 • $123,218 Cleaning • Initial cleaning and cleaned every 3 years (3% inflation) • Year 1 $13,250 • Year 4 $7,239 • Year 7 $7,910 • Year 10 $8,644 • Year 13 $9,446 • Year 16 $10.322 • $50,186 Takes you through Year 16 19 4/2/2012 Replacement Cleaning • Initial Replacement and replaced every 15 years (3% inflation) • Year 1 $26,500 • Year 15 $40 084 • Initial cleaning and cleaned every 4 years (3% inflation) • Year 1 $13,250 • Year 5 $7,457 • Year 10 $8,644 • Year 15 $10,021 • $66,584 • $32,746 Replacement • Large labor costs and long down time • Difficulty in gaining access to filters • Greensand up $100 cubic foot and may wait 6 months Cleaning • Can be too much build-up to clean efficiently • Some plants have issues with getting rid of backwash • Will do more often than replacement • No chance to repair under drains • GAC Media can be cleaned, but not regenerated 20 4/2/2012 • More water use during backwash • More Electricity used • More labor used because of more frequent backwash • Added chemical cost • More chlorine / phosphate, etc. needed post filter • Potentially more Bio-film growth in Towers and distribution system • Replace ? • Expensive • New • Still other issues potentially unattended • Clean • Generally less expensive • Like New • Cleans under drains, etc 21 4/2/2012 • Depending upon build-up • Clean every 1, 2, 3, or 4 years • What if there is no money to replace or fully clean? • Can partially clean to maintain usage and stay ahead of build-up • Actually a good way to save money • If current filters are in severe shape • Replace • Get on routine cleaning • Take numbers of years to get bad and divide by 60% to decide how often to clean Before Cleaning • Iron out of Filter – 2.0 + • Chlorine rotameter was set at 18 pounds per • Backwash contained high levels of dirty water • Full of mudballs and slime • Residential Complaints of Dirty Water 22 4/2/2012 • Iron out of Filter – .1 • Chlorine rotameter was set now at 13 – chlorine demand in filter decreased • Backwash contained now little or no iron after backwash • Now no slime and mudballs • Improved water quality fewer complaints less dirty water • Best One – Residents Happier – Supt. Sleeps better at night! Reducing TOCs, DBPs, and Improving Chlorine Residuals 23 4/2/2012 Where are the Biofilms and Organics? At the Reservoir In the Wells In the water mains from wells to Plant At the Aerators In the Treatment Plant In the Basins and Clearwells In the Towers In the Distribution System What is a Biofilm? • Adhere to surface and grow • They Feed Themselves • Live off bacteria in the water • Many types • Bacteria • Protozoa • Fungi • algae • Cover their “Colony” in a protective polysaccharide shield 24 4/2/2012 The Extracellular Matrix • Biofilm is held together by EPS • Extracellular polymeric substance • I say “polysaccharide shield” • Protects the biofilms cells • Resistance to chemicals, detergents, and antibiotics “Indicators” of Bioflim • High HPC • High Total Coliforms • High TOC • High AOC • High BDOC • High DBPs • Low Chlorine Residuals 25 4/2/2012 What is an organic? TOC – Total Organic Carbon • Measures total carbon and inorganic carbon • Decaying Vegetation • Bacterial growth • Metabolic activities of living organisms • Chemicals NOM – Natural Organic Matters • Part of TOC • Humic Acid • Fulvic acid • Amines & urea • React with Chlorine compounds to form Disinfection By Products • Fertilizers 26 4/2/2012 Why are biofilms and organics in all these places? Biofilms Organics • Aqueous Environment • Naturally occurring • Lots of nutrients • Synthetics • Organics • Detergents • Minerals • Pesticides • Added chemicals • Fertilizers • In hard to reach spots • Filters • Towers • Correlation between high TOCs and biofilm development • Distribution systems What are the Negative effects on your System? • Increase in Chemicals • Increase DBPs • TTHMs • HAAs • Low to zero Chlorine residuals • Burden on your Equipment • Aerators • Filters • Wells 27 4/2/2012 Is there a simple test? “Grab” sample • Biofilm may detach individually or in clumps • Testy may not indicate biofilms • Dynamic and respond to their environment What happens? • Biofilms over time survive • Bacteria will often die quickly without biofilm • Extra Cellular Matrix will may produce catalase to breakdown chemicals 28 4/2/2012 More Issues • Nitrification • Taste and Odor problems • Internal Corrosion and Loss of Flow due to biofilm deposition • Excessively High Applied Chlorine Rates • Dirty Water Complaints What Should I do? • Suggestion from the Experts • Montana State University • “Control of these biofilms is difficult. Disinfection alone is usually ineffective. Reduction of organic matter, improved disinfection, and the implementation of corrosion control in unlined iron pipes are present, or a combination of these methods is helpful in controlling distribution system biofilms.” - Camper, A.K MSU 29 4/2/2012 Algae - Isn’t this Lovely? Geeseweed? What Is Algae? True Algae are essentially Plants! – no toxins Cyanobacteria – release toxinsa • Cyanobacteria are a sub-category of bacteria that contain photosynthetic pigments, and therefore produce energy through photosynthesis • Previously known as blue-green algae. 30 4/2/2012 Cyanobacteria are very resilient and adaptive, existing virtually anywhere moisture can be found • Can be unicellular or colony-forming in nature. Colonies can be in the form of filaments, biofilms, or ‘ball type’ structures Cyanobacteria common in Illinois: • Anabaena • Aphanizomenon 31 4/2/2012 … Cyanotoxins • How cyanobacteria produce cyanotoxins is not fully understood • After a cyanobacteria dies, its cell wall decays (lyses) and releases its accumulated toxins into a water supply • Cyanotoxins can accumulate in other aquatic life (fish, shellfish) • Exposure to cyanotoxins can occur through direct contact or accidental ingestion What a cyanobacterial bloom looks like • Foam, scum, or mats • May be blue, bright green, brown, or red and may look like paint floating on the water. St. John’s River Charles River 32 4/2/2012 Multiplying Cyanobacteria • Cause blooms, & during blooms, water can become hypoxic, adversely affecting other aquatic life • Cyanobacteria also produce Taste and odor issues Health concerns in mammals (including humans) include: • Hepatotoxins (liver function) • Neurotoxins (nervous system functions) • Possible link to ALS (Lou Gehrig’s Disease) • Cytotoxins (damages individual cells) • Gastrointestinal distress (nausea, diarrhea) • Pruritic Skin Reactions (itching, rashes) 33 4/2/2012 And No fun Headlines No One wants to see Published: May 2, 2010 • Ft. Wayne Journal Gazette • Algae bloom fouls tap water in Indianapolis, Muncie • July 2, 2010 • Dayton Daily News • Grand Lake St. Marys 'dying' from toxic algae July 2011 • AssocTimes-Union – • Blue-green algae found in southern Kosciusko 34 4/2/2012 Simple Truths • When Algae grows, it increases pH • The increase pH forms carbonate • This leads to – • • • • • Increase in TOC Release of algae toxins Increase in DBP precursors Shorter filter runs Taste and odor issues What Can you Do? • Test • Notification of Illinois EPA • Treatment 35 4/2/2012 Testing Taste and Odor • Threshold Odor Test • Done by humans –water diluted until no odor is detectible • Flavor Profile Analysis • Determines which tastes are causing the odor Microcystin – LR • Collecting water samples: • When practical, sample is collected 1 ft. below the water surface • During blooms, surface samples (both water and biomass) are also tested What the Testing will Tell You • Algae count • Toxin concentration level • Algae Identification • pH & Turbidity 36 4/2/2012 Algal Toxin Thresholds Threshold (ug/L) Microcystin Anatoxin-a Cylindrospermopsin Saxotoxin Do Not Drink 1 20 1 0.2 Do Not Use 20 300 20 3 Potential Labs (Ohio EPA) Celina Utilitiesi GreenWater Labst Mike Sudman, Jr. Palatka, FL 419-586-2270 877-869-2542 cwtpsupt@bright.net info@greenwaterlab.com BSA Environmental Dr. Judy Westrick Beachwood, OH Lake Superior State 216-765-0582 906-635-2165 j.beaver@bsaenv.com jwestrick@Lssu.edu 37 4/2/2012 Other “Headlines” No One wants to see • TTHMs – MCL 80 • HAAs – MCL 60 TOC Reduction Chart Raw TOC 2.0 – 4.0 4.0 – 8.0 8.0 + 0-60 35% 45% 50% Raw Alkalinity 60-120 25% 35% 40% 120 + 15% 25% 30% 38 4/2/2012 $ your Village Manager doesn’t want to see • High Dollars being spent on Permanganate • High Dollars spent on Powdered Activated Carbon • High Dollars spent on Chlorine • You’re treating the Reservoir again with Copper Sulfate What can you Do? • Optimize Plant process • Chlorine • T & O associated with color and turbidity or floating algae, adjustments to coagulation, sedimentation, and filtration often work • Air Stripping • Oxidation • Mechanical • Chemically – more later 39 4/2/2012 Some Suggestions • Ohio EPA White Paper • June 9, 2011 • Through the Treatment Train Source Water Treatment • Watershed Protection • Reduce Nutrient Load • Reduce or eliminate contaminants • Algaecides • Earth Tec • Copper Sulfate • Treat Early • Potential for toxin release is low • If toxins released, easier to remove • Low pH 40 4/2/2012 Common Treatments Copper Sulfate • Copper Sulfate • Apply directly to Lake, Pond, or reservoir • Typically need “certified applicators” • GPS Devices specially designed boats • Drag burlap bag around • Inactivates Algae • Drops quickly to bottom of water basin Earth Tec vs Copper Sulfate in Reservoirs • Self- Disperses • 25 ft. horizontally & 8 ft. vertically per hour • 99.9 % Active Cu++ ion • More copper available to attack the problem 41 4/2/2012 Pictures you are looking for Conventional Treatments • Coagulation If these are good • Flocculation • Sedimentation Then, these work well • Filtration • Disinfection 42 4/2/2012 Coagulation and Flocculation • Good Preparatory step for removal • Guidelines • Control Targets for turbidity, DOCs, etc. • Do Jar tests to allow for differences in water quality • Minimize Flocculator speeds where possible • May have to increase Sedimentation sludge withdrawal cycles • Want to avoid dissolved toxin release from decaying cells Chlorine • Are you sure you want to chlorinate before filter influent? • Can Lyse blue-green algae cells and increase dissolved toxins • Proper application very good for many toxins • Does not effectively eliminate anatoxin-a • Chloramines are not effective for toxin destruction 43 4/2/2012 Filters • May increase backwash frequency • Avoid long storage times and decay inside filter bed • Check filter effluent for cell breakthrough • Minimize hydraulic disturbances • Consider Cleaning in Place procedure to remove deposits to improve filter performance • Less expensive than filter replacement Activated Carbon • Granular Activated Carbon (GAC) • Absorb toxins • Can be used as biological process by allowing bacterial growth on GAC media • Effectiveness influenced by type of toxins and competing Natural Organic Matter (NOM) • Consider optimizing reactivation frequency based on occurrence of blue-green algae • Life span 2 months to 1 year 44 4/2/2012 Powder Activated Carbon • Can be used periodically or seasonally • Can be added prior to coagulation and removed in settling tanks, or added to settling tanks and removed in filters • Need adequate detention time – 60 minutes • Many types • Coal - saxitoxins • Wood – micocystins & cylinsrospermopsin • Coconut - saxitoxins Oxidation • Preoxidation • Not recommended by Ohio EPA – not sure of Illinois • Will lyse blue-green algae cells and release their toxins • If Pre-Oxidation is necessary for adequate turbidity and / or organic carbon removal consider weaker oxidant such potassium permanganate • Use PAC to remove toxins released by permanganate • Oxidants may increase Disinfection Byproducts • Consider non-oxidizing organic removal programs – EarthTec – (Often Reduces Disinfection byproducts and TOCs) 45 4/2/2012 Chlorine • Reactive Against • Microcystins • Cylindrospermopsin • Saxitoxins – to a lesser extent • Not reactive vs. anatoxin –a • Reactivity influenced by pH and presence of NOM • Need more Contact time depending on water quality Chloramine & chlorine dioxide • Not reactive vs. the four toxins • Need very high doses and long contact time with chloramines effective vs. microcystins, but doses are not realistic • Effective doses of chlorine dioxide cause problems with chlorite and chlorate 46 4/2/2012 Potassium Permanganate • Reactive vs. • Microcystins • Anatoxin-a • Cylindrospermopsin – possibly • Not Oxidized • saxitoxin Ozone • Reactive vs. • Microcystins • Anatoxin-a • Cylindrospermopsin • Least susceptible • Saxitoxin • 20% of microcystins • Hydrogen Peroxide with Ozone better than Ozone alone 47 4/2/2012 UV • With Hydrogen Peroxide is effective • However, increased power requirement for advanced oxidation is many times greater than required for UV levels in water disinfection Earth Tec - Reducer • Removes precursors to • • • • Microcystins Cylindrospermopsin Anatoxin –a saxitoxin • No lysing of cell • Often Replaces Permanganate in treatment train • Often reduces feed rate of PAC and chlorine • Reduces DBPs • Clears basins of algae 48 4/2/2012 Membrane Filtration -others • Should remove blue-green algae effectively • Large pore size allows extracellular toxins to pass through • Cells may rupture • Extent depends on pressure and time between backwashes • Cells can hard to remove from membrane • Submerged systems may be better than pressurized systems Biological Filtration • Will remove/ inactivate • Microcystins • Cylindrospermopsin • Saxitoxin may transform to more potent toxin • Often difficult to manage – best used a “polishing step” following another primary removal treatment 49 4/2/2012 Residual Handling issues • Modify Backwash • Modify sludge recycling process • Too much of either process can cause unruptured cells to lyse • Discontinue during Bloom? • Remove sludge from sedimentation basins A Couple of Case Studies • Gateway Regional 50 4/2/2012 Gateway Regional – Case Study • New Program Started - May 3, 2010 2009 - Numbers • TOC Reductions July 44% 3rd 4th Qtr. Qtr. August 43% Sept. 52% THMs 75 48 Oct. 42% Nov. 50% HAAs 60 33 Gateway Regional – Case Study • New Program Started - May 3, 2010 2010 - Numbers • TOC Reductions July 53% 3rd 4th Qtr. Qtr. August 60% THMs 40 33 Sept. 44% Oct. 52% Nov. 64% HAAs 19 17 51 4/2/2012 Gateway Regional – Case Study • New Program Started - May 3, 2010 2011 - Numbers • TOC Reductions July ? 3rd 4th Qtr. Qtr. August ? THMs 41 29 Sept. ? Oct. ? Nov. ? HAAs 18 17 Gateway Regional – Case Study • Other Benefits • PAC reduced form 6-7 ppm to 2-3 ppm • Previous Taste and odor issues gone • Eliminated algae in clarifier troughs • Reduced Chlorine feed rate 52 4/2/2012 Salem, IL– Case Study • New Program Started – April 2010 2009 – Numbers – Avg. 4 sampling sites 1st Qtr. Qtr. rd 3 Qtr. 4th Qtr. 2nd THMs 62 60 64 82 HAAs 38 35 15 54 Salem, IL– Case Study • New Program Started – April 2010 2010 – Numbers – Avg. 4 sampling sites 1st Qtr. Qtr. rd 3 Qtr. 4th Qtr. 2nd THMs 43 84 15 25 HAAs 42 31 7 - New Program rolling 8 53 4/2/2012 Salem, IL– Case Study • New Program Started – April 2010 2011 – Numbers – Avg. 4 sampling sites 1st Qtr. Qtr. rd 3 Qtr. 4th Qtr. 2nd THMs 29 62 83 41 HAAs 24 40 23 - Algae Bloom 16 At The Well & Mains Work with your well company When to Clean 80% of original capacity Coliforms presence How to Clean Chemicals Super Chlorinate Aqua Gard EarthTec 54 4/2/2012 Iron Bacteria • Reddish or Brown slimy masses • Often produce “oily” sheen • Odors • Rotten eggs, fuel oil, cucumbers, or sewage • Corrosion of Equipment • Reduction in well yields • Increased infestations of other types of bacteria • Coliforms • Sulfur reducing bacteria At The Aerator Maintenance Iron Bacteria Dirty Labor Issues Increased Backwash of Softeners / Filters Burden on Filters Excess Iron / Mn to come through 55 4/2/2012 Pipe After Aerator Case History - Atlanta, IL • Dirty water Complaints • Aerator Cleaning hours, slimy gooey mess 5 guys, 8 • Softeners had slime and needed backwashing 3 times a day • No Chlorine Residuals on edge of town • Flushing took 3 weeks – 20 minutes a hydrant • Salt for Softeners ordered 14 times a year • $3,200 an order 56 4/2/2012 Case History - Atlanta, IL • “I don’t know what the hell you’re doing, but keep it up” • Took 2 summer help kids 2-3 hours and they weren’t even dirty • Backwash softeners once a day – Regenerate at 32,000 instead of 25,000 – crystal clear water • No Slime on top of softeners • Salt Order down 3 times in 6 months Atlanta, IL • Chlorine Residual 0.05 to 0.10 at edge of town • Flushing took 4 days – 10 minutes a hydrant • Iron levels were .6 - .8 - now .18 57 4/2/2012 In Basins & Clear wells Biofilms Organics Primarily Algae - SW • Increase DBPs • Extra $ on Permanganate, PAC, and chlorine • Time • “Eats” Chlorine • Low residuals • Increase DBPs Short Case Study – Speedway, IN • Algae Growth in Sedimentation Basins • Engineers recommended $500,000+ cover for basins • Chlorine Fed at beginning of basins • Heavy build up on sides of wall, dredging chains, and dark green color to water 58 4/2/2012 Short Case Study – Speedway, IN • Significantly less Algae Growth in Basins • Applying for permanent permit • Less Chlorine Fed at beginning of basins • No Heavy build up on sides of wall, dredging chains, and dark green color to water In the Distribution System • Disappearing Chlorine residuals • Higher Applied Chlorine Rates to achieve the same residuals • Dirty Water complaints • Slime on meters • Slimy Toilet tanks • Internal Corrosion 59 4/2/2012 In the Distribution System • Attack from the plant or from a booster station • Use Deposit Control Agents • Chloramines • Phosphates • Go after polysaccharide shield of biofilm • Must be on a flushing program • Automatic Flushers Corrosion • Stainless Steel • Microorganisms modify disposition of metals • Detach individually or in clumps • Migrate across surfaces • 10 fold more biofilm on metals vs. plastic 60 4/2/2012 Phosphate Phosphate #1 Price per gallon % phosphate $12.00 18% Phosphate #2 Price per gallon $12.00 % phosphate 35% weight in lbs 10.5 weight in lbs. 11.5 price per wet lb $1.14 price per wet lb $1.04 price per lb of Phosphate $6.35 price per lb of Phosphate $2.98 pounds used per day 46.33 pounds used per day 23.83 Gallons used per day 4.41 Gallons used per day 2.07 Cost per day $52.95 Cost per day$24.86 Two Ways to Chemically Approach Biofilm 1. Periodically, as a System Cleaning Agent. • Feed in conjunction with a System Flush 2. Continuously, after system cleaning lower dosage to small maintenance level • • Again, system cleaning should be done in conjunction with system flush 61 4/2/2012 New Product • Can penetrate slime layers, cell walls and protective layers of micro-organisms and effectively kills pathogens as a result. The micro-organisms will either die or suffer from reproductive failures. Summary • Biofilms and Organics may in every part of your system • Each Area may take a different approach • Often a combination of approaches is the best solution • Consultants, engineers, well drillers, and lab 62 4/2/2012 Summary • Blue-Green Algae is cyanobacteria • Releases Toxins • Not Easy to remove • One solutions may cause other issues • Consider new options Questions Mark McKee- (765) 719-2956 Dan Helm- (309) 236-7469 John Reynhout (815) 693-3694 Troy Mott (309) 824-9975 63