Water Treatment Processes Water Treatment Plant Operation Water Treatment Processes Section 1: Section 2: Section 3: Processes Section 4: Section 5: Section 6: Section 7: Section 8: Water Treatment Concerns Well Considerations Conventional Water System Disinfection By-Product Control Corrosion Control Demineralization Processes Coagulation Process Control Water Softening Florida Rural Water Association Water Treatment Plant Operation 2 Section 1: Water Treatment Concerns Microbial Contamination Concerns Barriers to Contaminants Reaching the Public Where Contamination Comes From Bacterial Indicators and Pathogens Primary Standards Secondary Standards Florida Rural Water Association Water Treatment Plant Operation 3 Microbial Contamination is Primary Concern of Water Operators Coliform bacteria Common in the environment and are generally not harmful but their presence in drinking water indicates that the water may be contaminated and can cause disease. Fecal Coliform and E coli Bacteria whose presence indicates that the water may be contaminated with human or animal wastes. Microbes in these wastes can cause short-term effects, such as diarrhea, cramps, nausea, headaches, or other symptoms. Turbidity Has no health effects. However, turbidity can interfere with disinfection and provide a medium for organisms that include bacteria, viruses, and parasites that can cause symptoms such as nausea, cramps, diarrhea, and associated headaches. Florida Rural Water Association Water Treatment Plant Operation 4 Multiple Barrier Approach Source: Selection and Protection Treatment: Methods and Efficiencies Florida Rural Water Association Water Treatment Plant Operation Distribution: Maintenance and Monitoring 5 Where Contamination Comes From Condition Test For: Reoccurring Gastro-illness* Coliform in Drinking Water Pipeline Failure pH, Lead, and Copper Nearby Agriculture Nitrates, Pesticides and Coliform Nearby Mining Metals and pH Nearby Landfill VOCs, TDS, Chlorides, & Sulfate Nearby Fueling VOCs Bad Taste/Odors Hydrogen Sulfide and Iron Stains Clothes/Plumbing Hydrogen Sulfide and Iron Scaly Residue Hardness * Multiple Sources, ie. runoff, septic tanks, CAFOs Florida Rural Water Association Water Treatment Plant Operation 6 Microbial Contaminants found in Surface Water or UDI Sources Cryptosporidium and Giardia Parasites that enters lakes and rivers through sewage and animal waste. These typically cause mild gastrointestinal diseases. However, the disease can be severe or fatal for people with severely weakened immune systems. EPA and CDC have prepared advice for those with severely compromised immune systems who are concerned about these organisms. Florida Rural Water Association Water Treatment Plant Operation 7 Some Facts About Bacteria Bacteria are widely distributed on earth They have been found 4 miles above earth and 3 miles below sea sediments. One gram of fertile soil contains up to 100,000,000 bacteria. Bacteria are inconceivably small and measured in microns. One micron is equal to 1/1,000,000 of a meter. During the rapid growth phase bacteria undergo fission (cell division) about every 20 to 30 minutes. One bacterial cell after 36 hrs of uncontrolled growth, could fill approximately 200 dump trucks. Florida Rural Water Association Water Treatment Plant Operation 8 Bacteria and Pathogenic Indicators in Water Treatment Total Coliform Ferment Lactose @ 35OC Include Species of Genera Fecal Coliform Citrobacter Enterobacter Klebsiella E. Coli Grow at 44OC Produce Enzyme More Specific Indicator of Contamination < 500 colonies/ml E. Coli HPC Photo: CDC. E. coli 0157:H7 11 of 140 cause gastrointestinal disease Identifying Source of Contaminants Florida Rural Water Association Water Treatment Plant Operation 10 Primary or Inorganic Contaminants Mineral-Based Compounds These include metals, nitrates, and asbestos. These contaminants are naturally-occurring in some water, but can also get into water through farming, chemical manufacturing, and other human activities. Potential health effects include learning disorders, kidney and liver damage. EPA has set legal limits on 15 inorganic contaminants. Florida Rural Water Association Water Treatment Plant Operation 11 Primary Standards and their Maximum Contaminant Levels (MCLs) Contaminant Arsenic Asbestos Fluoride Mercury Nickel Nitrate Nitrite Total Nitrate+Nitrite Sodium MCL (mg/l) 0.010 7 (MFL) 4.0 0.002 0.1 10 1 10 160 Florida Rural Water Association Water Treatment Plant Operation 12 Disinfectants and Disinfection By-Products Disinfectants are water additives that are used to control microbes Disinfection By-products are created when chlorine is added in the presence of naturally occurring low levels of organic materials found in drinking water Both are regulated because of health concerns Florida Rural Water Association Water Treatment Plant Operation 13 Secondary Standards and Concerns These compounds cause aesthetic concerns such as taste, odor and color. EPA recommends MCL limits Some states such as Florida have set regulatory limits on these contaminants Florida Rural Water Association Water Treatment Plant Operation 14 Secondary Standard Maximum Contaminant Levels Contaminant Chloride Sulfate TDS Copper Fluoride Iron Manganese Silver pH (MRCL) Color (MCRL) MCL (mg/l) 250 250 500 1.0 2.0 0.30 0.05 0.1 6.5 to 8.5 15 cfu Florida Rural Water Association Water Treatment Plant Operation 15 Protecting Well by Grouting Pressure Testing of Grout Seal @ ~10 psi for 1 hr. Should be Performed. Prevent movement of water between aquifer formations Preserve quality of producing zones Preserve Yield Prevent water intrusion from surface Protect Casing against Corrosion! Florida Rural Water Association Water Treatment Plant Operation 16 Section 2 Well Considerations Floridan Aquifer Well Contaminants Preventing Contamination at the Well Head Florida Rural Water Association Water Treatment Plant Operation 17 Floridian Aquifer Across Florida Florida Rural Water Association Water Treatment Plant Operation 18 Well Source Water Parameters Quality and Quantity Dictates Depth of Well TDS Total Hardness Total Fe and Mn Chlorides & Sulfates Total Alkalinity Nitrate pH Corrosivity CO2 H2S Fluoride Florida Rural Water Association Water Treatment Plant Operation 19 Preventing Contamination at the Well Head # Observation Likely Pathway 1 Septic tanks, broken storm or san. pipes, ponds Drainage up-hill Through Surface Strata Well subject to flooding Casing termination Surface water transport of contaminants Must be 1’ and above 100 20 yr flood plane 2 3 4 Surface water runoff Preventing Contamination at the Well Head (continued) # Observation Likely Pathway 5 Area around well is wet Possible Abandoned wells in area Sanitary condition unacceptable Cracking in Well Slab Corroded Casing Pipe 6 7 8 Surface water intrusion from contaminated source Contaminated water intrusion Contaminated water intrusion Florida Rural Water Association Water Treatment Plant Operation 21 Preventing Contamination at the Well Head (continued) # Observation 9 Evidence of Algae or Mold on Slab Poor Drainage 10 11 12 Likely Pathway Birds and insects attracted by moist conditions Surface water intrusion from contaminated source Seal water Draining Contaminated water into well head entering borehole Well Seal damaged Contaminated water intrusion Florida Rural Water Association Water Treatment Plant Operation 22 Preventing Contamination at the Well Head (continued) # Observation Likely Pathway 13 Fittings pointing upward Well vent not properly installed Check Valve absent or not working Cavitation or water hammer Contaminated Water intrusion into casing Contaminated Water intrusion into casing Contaminated water backflowing into casing Ck. Valve damage & water back-flowing into casing 14 15 16 Florida Rural Water Association Water Treatment Plant Operation 23 Preventing Contamination at the Well Head (continued) # Observation Likely Pathway 17 Well Site Security Compromised Livestock or wild animals close by Surface water evidence ID Several wells available Contaminated Water from undesirable activities Animal source of Contamination Indicator organisms, color, temp and TOC contributing One well is more likely to contribute than others 18 19 20 Florida Rural Water Association Water Treatment Plant Operation 24 Preventing Contamination at the Well Head (continued) # Observation Likely Pathway 21 Intermittent Well Operation 22 Wet or extreme weather events Contaminated occurring from long-term biological activity Contamination from run-off or from higher pumping levels. Florida Rural Water Association Water Treatment Plant Operation 25 Section 3: Conventional Water System Processes TOC in Source Water Disinfection and Uses of Chlorine Aeration and Aerator Types Iron and Hydrogen Sulfide Control Filtration Sedimentation Florida Rural Water Association Water Treatment Plant Operation 26 Organic Carbon (TOC) in Natural Waters mg/l Mean Surface Water 3.5 Sea Water Ground Water Surface Water Swamp Wastewater Wastewater Effluent .1 .2 .5 1.0 2 5 10 20 50 100 200 500 1000 Florida Rural Water Association Water Treatment Plant Operation 27 Disinfection with Chlorine The primary methods of disinfection is the use of chlorine gas, chloramines, ozone, ultraviolet light, chlorine dioxide, and hypochlorite. Generally Chlorine will be used by small systems and may be applied as a gas, solid or liquid. The most common chlorine application is sodium hypochlorite or bleach. Primary Disinfectants are used to inactivate microbes and Secondary Disinfectants are used to provide for a residual chlorine concentration that prevents microbial regrowth. Florida Rural Water Association Water Treatment Plant Operation 28 Reactions of Chlorine with Water Constituents Reducing Compound (inorganics) Production of Chloramines Production Chlororganics Combined Chlorine Breakpoint Chlorination Free Chlorine Residual Florida Rural Water Association Water Treatment Plant Operation 29 DISINFECTION BYPRODUCTS REMAIN Fe Mn H2 S 0.6 Add NH3 Dichloromine 0.2 Chloromine 0 0 Breakpoint Chlorination Curve Florida Rural Water Association Water Treatment Plant Operation 30 Other Chlorine Uses Chlorine is often used as an oxidant to remove inorganic impurities such as iron and hydrogen sulfide When used in this manner particulate matter is formed that often must be removed. Chlorine is also used to prevent the growth of algae on tank walls and other surfaces exposed to sunlight and to prevent bacteria from growing inside filters and tanks Chlorine has been used to remove color, taste and odors but will produce disinfection by-products which are regulated Florida Rural Water Association Water Treatment Plant Operation 31 Aeration Aeration is generally used in small systems to remove naturally occurring dissolved gasses from the water such as CO2 and H2S. Aeration may also be used to oxidize iron which then drops out as precipitate and must be filtered. Special aerators called Packed Towers are sometimes used to remove VOCs Florida Rural Water Association Water Treatment Plant Operation 32 Cascade Tray Aerator Even distribution of water over top tray Loading Rates of 1 to 5 GPM for each sft. of Tray area. Trays ½” openings perforated bottoms Protection from insects with 24 mesh screen Florida Rural Water Association Water Treatment Plant Operation 33 Forced Draft Aeration System Includes weatherproof blower in housing Counter air through aerator column Includes 24 mesh screened downturned inlet/outlet Discharges over 5 or more trays Florida Rural Water Association Water Treatment Plant Operation 34 Packed Tower Odor Removal System Uses Henry’s Law constants for mass transfer Usually requires pilot testing Used to Remove VOCs below MCL Col to Packing >7:1 ratio Air to water at pk >25:1 with max 80:1 Susceptible to Fouling from CaCO3 > 40 PPM Florida Rural Water Association Water Treatment Plant Operation 35 Iron Problems - Most Prevalent in Unconfined, Surficial, and Biscayne Aquifers Iron dissolved by reaction with CO2 Iron from well sources will be in a dissolved state When exposed to O2 precipitants form Visible as red and brown color Will stain fixtures and clothes Imparts taste and odor Florida Rural Water Association Water Treatment Plant Operation 36 Iron, Turbidity/TOC Relationships Florida Rural Water Association Water Treatment Plant Operation 37 Dissolved Iron Problems Soluble iron passing into the water distribution system will encourage the growth of iron bacteria Precipitates will form in the distribution system Iron particles will stain clothes and fixtures (Red Water Complaints) Florida Rural Water Association Water Treatment Plant Operation 38 Treatment of Dissolved Iron Type of Treatment Removal Considerations Oxidation w/ Chlorine Greensand Filter Ion Exchange Softener Phosphate Addition Max. 0.1 mg/l w/o filtration 0 – 10 mg/l w/ pH > 6.8 0 – 10 mg/l 0 – 2 mg/l Florida Rural Water Association Water Treatment Plant Operation 39 Fe ++ Aeration Plot of pH vs. Time for Iron Removal at 90% Efficiency (min 30 minutes detention) Florida Rural Water Association Water Treatment Plant Operation 40 Filtration Requirements for Iron and Manganese Requires bé DEP at > 1.0 mg/l Fe Turbidity must be no more than 2 NTUs above Source Water Oxidized particles must generally be removed Anthracite filters are frequently employed with higher iron content Florida Rural Water Association Water Treatment Plant Operation 41 Hydrogen Sulfide Removal Techniques (DEP) Sulfide (mg/l) Recommended Treatment Process Achievable Range of Removal < 0.3 Direct Chlorination 100% > 0.3 100% 0.3 to 0.6 Direct Chlorination (requires filtration) Conventional Aeration 0.6 to 3.0 Forced Draft Aeration 90% > 3.0 Packed Tower Aeration > 90% Florida Rural Water Association Water Treatment Plant Operation 50% 42 Hydrogen Sulfide Removal Dynamics Gas Soluble Florida Rural Water Association Water Treatment Plant Operation 43 Clarification Clarifiers are often used in water treatment to allow particles to settle prior to filtration. Special clarifiers called “Upflow Clarifiers” are used in surface water treatment plants that used coagulants and in softening plants that use lime. These types of clarifiers perform several treatment processes in one tank Florida Rural Water Association Water Treatment Plant Operation 44 Causes of Poor Clarifier Performance If Surface water plant flocculators are not adjusted for rate of flow Sludge removal is not routine There is no test to control sludge quantities Settled water turbidities are not measured or are not measured routinely (e.g., minimum of once per shift) Florida Rural Water Association Water Treatment Plant Operation 45 Filtration Filters are primarily used to remove particulate matter and turbidity from the water. The primary types of filters used in water treatment are Rapid Sand or gravity and Pressure Filters Special Membrane Filters are used for Particulate and Microbial removal. Special Filters employ Resins and Media such as greensand and are used to remove select contaminants such as iron and manganese. Activated carbon filters are used to remove organic compounds. Florida Rural Water Association Water Treatment Plant Operation 46 Nanofiltration Filter Applications Florida Rural Water Association Water Treatment Plant Operation 47 Media Configurations for Gravity Filters Single media (sand) Dual Media (sand and anthracite) Mixed or multimedia (sand, anthracite and garnet) Florida Rural Water Association Water Treatment Plant Operation 48 Characteristics of Various Filters Filter Media Sz (mm) Spec Grav Depth Flow Flow gpm/sf (in) Slow Sand Fine Sand 0.2 2.6 36 – 48 Gravity .05 - .03 Rapid Sand Course Sand 0.35 – 1.0 2.6 24 – 36 Gravity 2– 4 Dual Media Anthracite Sand 0.9 – 1.2 0,4 – 0,55 1.4 – 1.6 2.6 18 – 24 6 – 10 Gravity 4– 5 Mixed Media Anthracite Sand, Garnet 0.9 – 1.2 0,4 – 0,55 0.2 1.4 – 1.6 2.6 4.2 16.5 9 4.5 Gravity 5 Diatom. Earth Diatomaceous 0.005 to 0,125 1/16 to 1/8 Pressure or Vacuum 0.5 – 5 Pressure All Media Application Pressure 2– 4 49 Calculating Filter Flow Rate 1. 2. Determine Surface Area of Filter Measure Filter Rise with stopwatch and tape measure (often meters are out of calibration) Example: 150 sft surface area, 10.7” rise in 20 seconds (10.7 in / 12 in/ft) x 150 sft x 7.48 gal/cft = 1000 gal. (20 seconds / 60 min ) = 0.333 min Flow Rate = 1000 gal / 0.333 min 150 sf = Florida Rural Water Association Water Treatment Plant Operation 20 gpm / sft 50 Causes of Poor Filter Performance Filter Problems: operational, mechanical equipment failure, media failure Turbidity Errors: calibration, air bubbles, debris Chemical Feed Failures: coagulant, coagulant aid, filter aid Poor Water Quality: increased turbidity, algae Operating Plant intermittently exceeding peak loading capacity Florida Rural Water Association Water Treatment Plant Operation 51 Common Filter Operation Deficiencies Filters are started dirty (i.e., without backwashing Increases in plant flow Filter to waste rate made with no capability is not being consideration of filtered used or not monitored if water quality utilized Filters removed from service without reducing plant flow, resulting in overload Operations staff backwash the filters without regard for filter effluent turbidity Backwash rate too low for longer period or stopped early to conserve water No testing of filters resulting in media loss, underdrain or support gravel damage Significant build up of mudballs in filter media Individual filtered water quality is different and quality is not monitored Performance following backwash is not monitored or recorded. There are no records available which document performance Calibration procedures are not practiced Florida Rural Water Association Water Treatment Plant Operation 52 Filter Integrity Testing Evaluates filter media, support gravel and underdrains Check for filter depth, surface cracking, mudball and segregation Media is checked by excavation Steel rod is used to probe support gravel location and uniformity (should vary < 2”) Observe clearwell for evidence of media Check for uneven flow splitting to filters Florida Rural Water Association Water Treatment Plant Operation 53 Backwash Parameters Typically at about 24 hour intervals Rate: 15 gpm/sft – 20 gpm/sft Expand at min. 25% Backwashing Duration: 5 - 10 min. Filter to waste for 3 - 5 min. Water used for backwashing: 2% - 4% per filter of total water produced Florida Rural Water Association Water Treatment Plant Operation 54 Sand Filter ~40% Multimedia ~25% Deep Bed ~50% 15 to 20 gpm/sft Min. Expansion 25% Florida Rural Water Association Water Treatment Plant Operation 55 Determining Backwash Expansion in Plant Can be made with tin can lid Florida Rural Water Association Water Treatment Plant Operation 56 Visual Identification of Filter Problems Mudballs – Formed by chemical deposits of solids during backwashing (leads to coating of media surfaces) Surface Cracking – Caused by compressible matter around media at surface Media Boils – Caused by too rapid of backwash and displaces gravel support below Air Binding – Caused by excessive headloss (infrequent backwashing) allowing air to enter media from below Florida Rural Water Association Water Treatment Plant Operation 57 Section 4 Disinfection By-Product Control Disinfection By-Product Formation Factors Affecting By-Product Formation Locating THM and HAA5 Areas Formation of THMs and HAA5s Controlling Disinfection By-Products Importance of Water Age Flushing Methods and Benefits Florida Rural Water Association Water Treatment Plant Operation 58 Disinfection By-Product (DBP) Formation Disinfection Byproducts (DBP) are produced by the reaction of free chlorine with organic material found in natural waters. The amount of organic materials in a natural water called NOM can be approximated by the amount of Total Organic Carbon (TOC) present in the water source. NOM consists of various chemical compounds containing carbon, originating from decayed natural vegetative matter found in water. Florida Rural Water Association Water Treatment Plant Operation 59 Factors Affecting Disinfection By-Product Production Turbidity and the type of NOM present Concentration of Chlorine added pH of water Bromide Ion Concentration Temperature Contact Time Florida Rural Water Association Water Treatment Plant Operation 60 Locating TTHM Areas High Water Age Storage Tanks do not fluctuate No / Few Customer Areas Stagnant Areas Dead Ends Bad Pipe Regrowth Areas Pipe Tuberculation with Bacterial Growth producing Organic Precursors Florida Rural Water Association Water Treatment Plant Operation 61 Locating HAA5 Areas Low Demand Areas Toward Middle System Areas w/ Stagnant / Low Water Age Areas with No / Little Regrowth – Eliminate Biodegradation Locations – Free Chlorine Residuals < 0.2 mg/L – HPC Data No Dead Ends Florida Rural Water Association Water Treatment Plant Operation 62 Formation of DBP in a Water System 63 Disinfectant and DBP Production in a Typical Water System 64 DBP Reduction Techniques in a Water Distribution System Reducing detention time in storage tanks, Ensuring turnover in distribution system Flushing dead-end lines. Florida Rural Water Association Water Treatment Plant Operation 65 Typical Distribution System Water Age (Days) in Pipelines Population Miles of WM Water Age > 750,000 > 1,000 1 – 7 days < 100,000 < 400 > 16 days < 25,000 < 100 12 – 24 days AWWA: Water Age for Ave and Dead End Conditions Florida Rural Water Association Water Treatment Plant Operation 66 There are Two Types of Flushing Used by Water Distribution Systems Conventional Flushing & Unidirectional Flushing < 2.5 fps velocity that reduces water age, raises disinfectant residual removes coloration > 2.5 fps velocity that removes solid deposits and biofilm from pipelines 67 How Often to Flush • Dead-end mains at least monthly • Other flushing points at least twice annually (DEP requires quarterly flushing) • At intervals necessary to maintain consistent water quality throughout the distribution system • Often enough to maintain adequate disinfection residuals throughout the distribution system • Whenever Customer complaints of bad taste, odor, clarity or turbidity are received (DEP requirement) Florida Rural Water Association Water Treatment Plant Operation 68 Flushing Benefits Summarized • Restores disinfectant residual • Maintains or improves water quality a. Reduces bacterial growth b. Reduces customer complaints • Restores flow and pressure in the distribution system a. Reduces sediment b. Reduces corrosion and tuberculation in mains • Reduces DBP problems and lowers disinfection costs • Reduces pipeline maintenance costs • Increases life expectancy of the distribution system • Typically results in a fire hydrant maintenance program Florida Rural Water Association Water Treatment Plant Operation 69 Section 5 Corrosion Control Corrosion Control Methods Factors Affecting Corrosion Corrosion Tuberculation Example pH and Alkalinity Relationships Langerlier Index Troubleshooting Corrosion Complaints Basics of Sequestering Florida Rural Water Association Water Treatment Plant Operation 70 Corrosion and Chemical Activity Most all forms of corrosion are chemical reactions (erosion is the exception) that require three things: 1. 2. 3. A carrier such as Water that allows the movement of positively charged ions (from Anode+ to Cathode-) A condition (water metal contact) that allows metals to disassociate (ionize) and allows electrons to flow An imbalance that favors the transport of metals or ions to achieve a chemical balance in a water solution. Florida Rural Water Association Water Treatment Plant Operation 71 Corrosion Control Methods Corrosion Control is employed in water treatment to protect pipeline materials, appurtenances and fittings from leaching problematic (iron) and/or dangerous inorganic chemicals (lead and copper). Three types of treatment are generally used: 1.) Chemical Adjustment, Water Treatment and Sequestering Protection Measures in water system include the use of sacrificial metals and electronic cathodic protection. Florida Rural Water Association Water Treatment Plant Operation 72 Factors Affecting Corrosion Water’s pHs Water alkalinity Solids content Temperature Materials Used for pipes and other fittings. Florida Rural Water Association Water Treatment Plant Operation 73 Cathodic Action Resulting in Tuberculation in Water Pipelines Inside Pipe Wall 1.5” 74 Effects of pH on the Rate of Corrosion of Iron in Water Florida Rural Water Association Water Treatment Plant Operation 75 Relationships between Alkalinity, pH A Water can be Corrosive or Depositing based upon it’s pH and Alkalinity. Florida Rural Water Association Water Treatment Plant Operation 76 Affects of Raising or Lowering Alkalinity and CO2 by Chemical Addition Florida Rural Water Association Water Treatment Plant Operation 77 Determining pH of Water (Alkalinity in mg/l as pH = log {2.2 x 10 X CaCO3)} 6 (CO2 in mg/l) Measured Alkalinity 60 mg/l as CaCO3 pH = log Measured CO2 = 7.4 mg/l 6 {2.2 x 10 X 60/7.4 } = 7.25 Approximate pH between 7.0 to 8.0 Florida Rural Water Association Water Treatment Plant Operation 78 Use of the Langerlier Index for Determining Water Stability Every water has a particular pH value where the water will neither deposit scale nor cause corrosion. A stable condition is termed saturation. Saturation (pHs), varies depending on calcium hardness, alkalinity, TDS, and temperature. The Langerlier Index = pH – pHs Corrosive < LI = 0 > Scale Forming Florida Rural Water Association Water Treatment Plant Operation 79 Recommended Treatment for Corrosive and Scaling Water based on LI Saturation Index -5 -4 -3 -2 -1 -0.5 0 0.5 Description General Recommendation Severe Corrosion Treatment Recommended Severe Corrosion Treatment Recommended Moderate Corrosion Treatment Recommended Moderate Corrosion Treatment May Be Needed Mild Corrosion Treatment May Be Needed None- Mild Corrosion Probably No Treatment Near Balanced No Treatment Some Faint Coating Probably No Treatment 1 2 3 Mild Scale Coating Treatment May Be Needed Mild to Moderate Coatings Treatment May Be Needed Moderate Scale Forming Treatment Advisable 4 Severe Scale Forming Treatment Advisable Florida Rural Water Association Water Treatment Plant Operation 80 Troubleshooting Customer Complaints caused by Corrosion Water Characteristic Red/reddish-brown Water Blueish Stains on fixtures Black Water Foul Tastes and Odors Loss of Pressure Lack of Hot Water Reduced Life of Plumbing Tastes Like Garden Hose Likely Cause Distribution Pipe Corrosion Copper Line Corrosion Sulfide Corrosion of Iron By-Products of Bacteria Tuberculation Scaling Pitting from Corrosion Backflow From Hose Florida Rural Water Association Water Treatment Plant Operation 81 Sequestering Action of Poly and Ortho Phosphates Florida Rural Water Association Water Treatment Plant Operation 82 Polyphosphates for Sequestering Soluble Iron and Manganese after Treatment The Polyphosphate, Hexametaphosphate is commonly used for Sequestering Soluble Iron and Manganese Sequestering is used when soluble Iron and Manganese exists after treatment; The Agent is added after sedimentation Large doses (>5 mg/l) will soften rust deposits in pipelines which are transported into homes Proper dose is to keep soluble iron and/or manganese tied up for 4 days Florida Rural Water Association Water Treatment Plant Operation 83 Use of Orthophosphates for Sequestering Orthophosphate is used to sequester iron ions at pipe surfaces The Sequestering forms a protective coating that prevents further iron migration Ortho/Poly Blends provide both sequestering of soluble iron and iron movement from pipelines under corrosive conditions Florida Rural Water Association Water Treatment Plant Operation 84 Section 6: Demineralization Processes Basic Demineralization Systems RO Operating Considerations Pretreatment; Fouling and Scaling Issues Ion Exchange Considerations Sodium/Calcium Exchange Florida Rural Water Association Water Treatment Plant Operation 85 Ion Exchange, Membrane Filtration and Electrodialysis Several special treatment processes are used to remove selected mineral contaminants from the water. These include Ion Exchange, Membrane Filtration and Electrodialysis. These systems remove selected salts such as sodium, hardness consisting of Calcium and Magnesium and removal of selected contaminants such as Nitrate or Arsenic Florida Rural Water Association Water Treatment Plant Operation 86 Reverse Osmosis (RO) Treatment Considerations Used to Remove Highly Concentrated Salts (TDS) Operating pressure < 400 psi Salt Rejection Rates of < 95% Turbidity <1 NTU Flux Range 15 – 32 GFD (gallons Flux per day per sq. ft. membrane surface) Florida Rural Water Association Water Treatment Plant Operation 87 Pretreatment Requirements for Reverse Osmosis Systems Suspended Particulates Colloidal materials Microbiological Matter Chlorine Carbonates Sulfate Silica Iron Hydrogen Sulfide Blockage Filtration Fouling Coagulation/Filtration Fouling Chlorine Failure GAC or Dechlorination Scaling pH adjust or Softening Scaling Inhibitor or Cation Rem. Scaling Softening Scale/Foul Greensand (no aeration) Scale/Foul Degasification Florida Rural Water Association Water Treatment Plant Operation 88 Operating Considerations Ion Exchange Softening Iron and Manganese Corrosiveness of Brine Solution Pump Strainer Fouling of Resin Florida Rural Water Association Water Treatment Plant Operation 89 Optimal Water Characteristics for Ion Exchange pH NO3 SO4 TDS Turbidity 6.5 – 9.0 < 5 mg/l < 50 mg/l < 500 mg/l < 0.3 NTU Selectivity Considerations S04-2 > NO3-2 > CO3-2 > NO2-2 > CL-1 Florida Rural Water Association Water Treatment Plant Operation 90 Sodium Exchange MCL Considerations Sodium provides 100% exchange for Ca++ and Mg++ NaZeolite + Ca++ --> CaZeolite + Na+ and NaZeolite + Mg++ --> MgZeolite + Na+ For every grain (17.1 grains = 1 mg/l) of hardness removed from water, about 8.6 mg/1 of sodium is added. Sodium MCL = 160 mg/l - Initial Na water concentration + NaOCl 5 grains needed for corrosion control (86 mg/l) thus: source water hardness limit ~ 350 mg/l hardness (~20 grains) ie. 100% x 5 grains, or 15 grains removed x 8 = 134 mg/l Na 20 grains Provides 134 mg/l Na and 5 grains or 86 mg/l Hardness Florida Rural Water Association Water Treatment Plant Operation 91 Section 7 Coagulation Processes Control Metal Charges and Electron Attraction Elemental Weights and Chemical Formulas Particle Chemistry and Colloidal Particles The Floc Building Process Optimizing the Coagulation Process Use of a Jar Test Florida Rural Water Association Water Treatment Plant Operation 92 Periodic Table of the Elements Valances are shown at the top of the Periodic Table, F is one electron short and Mg has two extra electrons 93 The Periodic Chart also Provide the Atomic Weight of an Element 8 Includes Isotopes Atomic Number O Symbol Oxygen Name Use 16 15.99 Atomic Weight 94 Solids and Colloidal Material Suspended Solids Colloids Suspended in the Water and can be Removed by Conventional Filtration Finely Charged Particles that do not Dissolved Turbidity The Cloudy Appearance of Water caused by Suspended Matter and Colloids Electrical Charge of a suspended particle Zeta Potential Florida Rural Water Association Water Treatment Plant Operation 95 Primary Coagulants Primary coagulants are lime, aluminum sulfate (alum), ferrous sulfate, ferric sulfate and ferric chloride. These inorganic salts will react with the alkalinity in the water to form insoluble flocs which will trap the suspended matter in them. Florida Rural Water Association Water Treatment Plant Operation 96 Removal of Colloidal Particles by Coagulation & Flocculation Floc Building Process : Neutralization of repulsive charges Precipitation with sticky flocs Bridging of suspended matter Providing “agglomeration sites” for larger floc Weighting down of floc particles Florida Rural Water Association Water Treatment Plant Operation 97 Polymers and Ionic Charges Bridging Action of Cationic Polymer with Colloidal Particles Cationic + *Anionic Nonionic * Used with Metal Coagulants in water treatment Florida Rural Water Association Water Treatment Plant Operation 98 Factors Affecting the Coagulation Process pH (pH Range: Al, 5 – 7 ; Fe, 5 – 8) Alkalinity of water (> 30 PPM residual) Concentration of Salts (affect efficiency) Turbidity (constituents and concentration) Type of Coagulant used (Al and Fe salts) Temperature (colder requires more mixing) Adequacy of mixing (dispersion of chemical) Florida Rural Water Association Water Treatment Plant Operation 99 Jar Test Plot for Low Alkalinity or Low Turbidity Water Alum initially reacts with low alkalinity With Ferric Chloride requires chemical to reach optimal pH before reacting Adding too much coagulant increases turbidity Florida Rural Water Association Water Treatment Plant Operation 100 Section 8: Hardness and Water Softening Hardness Removal by Softening Treatment Methods Used to Remove Hardness Alkalinity Definitions Alkalinity/Acidity Relationships pH and Lime Treatment Removal of Color and Organics Importance of Recarbonation Florida Rural Water Association Water Treatment Plant Operation 101 Water Hardness Hardness in Water causes scaling, causes fibers in clothes to become brittle and increases the amount of soap that must be used for washing Hardness in water is caused by the water’s Calcium and Magnesium Content Water is considered hard when it has a hardness concentration of > 100 mg/l expressed as calcium carbonate equivalent Water that hardness < 100 mg/l expressed as CaCO3 is considered soft Hardness can either be removed by water treatment or sequestered using phosphates Florida Rural Water Association Water Treatment Plant Operation 102 Methods of Removing Hardness Treatment Method Hardness Levels Retained Lime Softening (Chemical Precipitation) RO (Nanofiltration) (Membrane Filtration) Ion Exchange (Chemical Exchange) Solubility Level of about 35 mg/l (CaCO3) 85 – 90% removal Basically Zero Water must be blended Florida Rural Water Association Water Treatment Plant Operation 103 Alkalinity Definitions The capacity of water to neutralize acids. The measure of how much acid must be added to a liquid to lower the pH to 4.5 It is caused by the water’s content of carbonate, bicarbonate, hydroxide, and occasionally borate, silicate, and phosphate. In natural waters, Alkalinity = Bicarbonate Hardness = Total Carbonate Hardness Florida Rural Water Association Water Treatment Plant Operation 104 Relationships among pH, Alkalinity and Indicators 0% 100% Bicarbonate and Carbonate Bicarbonate CO2 Carbonate and Hydroxide T Alkalinity T=0 P Alkalinity P=0 pH CaCO3 9.4 100% 10.2 Florida Rural Water Association Water Treatment Plant Operation Mg(OH)2 10.6 105 Types of Alkalinity that can be Present at pH Values Below 4.5 only CO2 present, no Alkalinity Between 4.5 to 8.3 only Bicarbonate present Between 8.3 to 10.2 Bicarbonate & Carbonate. Between 10.2 to 11.3 Carbonate & Hydroxide At 9.4 Calcium Carbonate becomes insoluble and precipitates At 10.6 Magnesium Hydroxide becomes insoluble and precipitates Florida Rural Water Association Water Treatment Plant Operation 106 Removal of Organics by Lime Softening Precipitation Calcium Carbonate 10% to 30% of Color, TOC & DBP Magnesium Hydroxide 30% to 60% of TOC & DBP and 80% of Color Addition of Alum/Ferric +5% to +15% of Color, TOC & DBP Sequential Treatment Additional Removal Color, TOC and DBP Florida Rural Water Association Water Treatment Plant Operation 107 Recarbonation in Lime Softening Because water has unused lime (calcium hydroxide) and magnesium hydroxide in solution at high pH (pH 11), these must be converted to a stable forms. CO2 is added to reduce Ca(OH)2 to CaCO3 which precipitates at about pH 10; additional CO2 is added to convert Mg(OH)2 to soluble Mg(HCO3)2 which occurs at a pH of 8.4. Reaction must be completed before filtration so that calcium carbonate will not precipitate in the filters or carry into distribution system. Florida Rural Water Association Water Treatment Plant Operation 108 Water Treatment Summary Effective Water Treatment Requires the application of accepted principles Most Process Problems in Water Treatment are the result of failure to recognize the symptoms that result from improper application or adherence to these factors Most treatment plant problems can be resolved by application of the techniques presented Florida Rural Water Association Water Treatment Plant Operation 109