do cation exchange systems affect the chlorination process
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Do Cation Exchange Systems Affect the Chlorination Process? - PowerPoint PPT Presentation

Do Cation Exchange Systems Affect the Chlorination Process? Presented By: Jeffrey W. Freeman, P.E., CFM, LEED AP Engineering Enterprises, Inc. March 22, 2016 Presentation Overview Ebony-Ammonia & Ammonium- Ivory Gimme A Breakpoint Holy


  1. Do Cation Exchange Systems Affect the Chlorination Process? Presented By: Jeffrey W. Freeman, P.E., CFM, LEED AP Engineering Enterprises, Inc. March 22, 2016

  2. Presentation Overview Ebony-Ammonia & Ammonium- Ivory Gimme A Breakpoint Holy # of Test Methods Cation Exchange Treatment Exposed

  3. Presentation Overview (Cont.) Evidence More Evidence Take That, Variable Ammonia! Acknowledgements and Q&A

  4. Ebony-Ammonia & Ammonium-Ivory

  5. Ebony-Ammonia & Ammonium-Ivory  Ammonia Dissolution In Water pK a = 9.25 + + OH - NH 3 + H 2 O  NH 4 Ammonia Ammonium  Total Ammonia  NH 3 + NH 4 +  Free Ammonia  NH 3 Only

  6. Ebony-Ammonia & Ammonium-Ivory Ammonia & Ammonium Dissolution pH = 9.25; Temperature = 20 O C 9.25 Source: Manual for Bosanska Krupa Nov. 2009

  7. Ebony-Ammonia & Ammonium-Ivory Ammonia & Ammonium Dissolution pH = 9.25; Temperature = 20 O C 7.5 Source: Manual for Bosanska Krupa Nov. 2009

  8. Ebony-Ammonia & Ammonium-Ivory Chloramine Chemistry  Monochloramine Development NH 3 + HOCl  NH 2 Cl + H 2 O  Dichloramine Development NH 2 Cl + HOCl  NHCl 2 + H 2 O  Nitrogen Trichloride Development NH 2 Cl + HOCl  NCl 3 + H 2 O

  9. Gimme a Breakpoint

  10. Gimme a Breakpoint Breakpoint Chlorination Overview Hump Total Chlorine Residual Breakpoint Chlorine Added

  11. Gimme a Breakpoint Breakpoint Chlorination Overview (Cont.) Monochloramine Monochloramine Dichloramine To Dichloramine Development To N ‐ Trichloride Total Chlorine Residual Total & Free Ammonia Total Total Free Ammonia Chlorine Chlorine Total Chlorine Nitrogen Free Trichloride Ammonia Chlorine Added

  12. Gimme a Breakpoint Breakpoint Chlorination Overview (Cont.) Cl 2 :NH 3 ‐ N<5:1 Cl 2 :NH 3 –N>5:1 Cl 2 :NH 3 –N>7.6 ‐ 9:1 Monochloramine Monochloramine Dichloramine To Dichloramine To N ‐ Trichloride Total Chlorine Residual Total & Free Ammonia Total Total Free Ammonia Chlorine Chlorine Total Chlorine NItrogen Free Trichloride Ammonia Cl 2 :NH 3 –N = 5:1 Cl 2 :NH 3 –N = 7.6 ‐ 9:1 Chlorine Added

  13. Gimme a Breakpoint  Five (5) Recommended Parameters To Confirm Breakpoint Has Been Achieved:  Free Ammonia  Total Ammonia  Monochloramine  Total Chlorine  Free Chlorine

  14. Holy # of Test Methods

  15. Holy # of Test Methods  Typical Ammonia Test Methods  Nessler Method: No Longer Standard Method Approved  Salicylate Method: Recommend For Total Ammonia  Indophenol Method: Recommend For Free Ammonia & Monochloramine  Ion Selective Electrode: Ideal Method For Precision, But Higher Capital & O&M Costs

  16. Holy # of Test Methods  Typical Chlorine Test Methods  DPD (N,N Diethyl-1,4 Phenylendediamine Sulfate)  Recommended For Total Chlorine and Free Chlorine, If Breakpoint Achievement Has Been Confirmed  Used With Many Test Kits/Analyzers  Free Chlorine Must Be Read Within a Minute of Sample Preparation  Total Chlorine To Be Read Within 3 – 5 Minutes After Sample Prepared  Indophenol  Recommended For Free Chlorine Confirmation  It Is Not An IEPA Approved Method For Free Chlorine Measurement

  17. Holy # of Test Methods  DPD Free Chlorine Test Method Additional Comments  Chloramines Are Known To Interfere With the Free Chlorine DPD Method  The Longer The Sample Sits, the Greater the Amount of Interference Occurs  DPD Method Is Accurate When Chloramines Are Not Present Excerpts From Hach DPD Free Chlorine Test Method Instructions

  18. Holy # of Test Methods  Indophenol Free Chlorine Test Method Additional Comments  It Is Not An IEPA Approved Test Method  Chloramines Do Not Interfere With Method  It Is a Good Check To Confirm Past Breakpoint Excerpts From Hach Indophenol Free Chlorine Test Method Instructions

  19. Cation Exchange Treatment Exposed

  20. Cation Exchange Treatment Exposed  Cation Exchange Treatment Summary  General Definition of Ion Exchange Treatment (Source: New Hampshire Department of Environmental Services): Ion exchange (IE) is a water treatment method where one or more undesirable contaminants are removed from water by exchange with another non- objectionable, or less objectionable substance. Both the contaminant and the exchanged substance must be dissolved and have the same type (+,-) of electrical charge.  Cation Exchange (CE) Treatment Targets Cations  Ions With + Charge  Typical Regenerant is Sodium Chloride (NaCl)

  21. Cation Exchange Treatment Exposed Typical Target Cations In NE IL +1 +2 Sodium Hardness Copper 2+ Cations Iron 2+ Zinc 2+ Barium & Radium Lead 2+ Source: http://science notes.org/use ‐ periodic ‐ table/

  22. Cation Exchange Treatment Exposed Affinity ( / əˈ fin ə dē/ ) : [Biochemistry] the degree to which a substance tends to combine with another. (Source: www.google.com) Source: Water Quality & Treatment, AWWA

  23. Cation Exchange Treatment Exposed Ion Exchange General Exchange Process HARDNESS CATIONS Ca 2+ Ca 2+ Ca 2+ Mg 2+ Mg 2+ Mg 2+ Ra 2+ Radium Na + Na + Na + Na + Na + Na + Barium Ba 2+ Na + Na + Na + Na + Schematic Calcium Ca 2+ Na + Cation Na + Exchange Na + Na + Magnesium Mg 2+ Resin Bead Na + Na + + Ammonium Na + NH 4 Na + Na + Na + Na + Na + Na + Sodium Na +

  24. Cation Exchange Treatment Exposed Ion Exchange General Exchange Process RADIUM & BARIUM CATIONS Ra 2+ Ra 2+ Ba 2+ Ba 2+ Ra 2+ Radium Na + Na + Mg 2+ Ca 2+ Barium Ba 2+ Mg 2+ Ca 2+ Schematic Calcium Ca 2+ Cation Mg 2+ Ca 2+ Exchange Resin Bead Magnesium Mg 2+ Na + Na + + Ammonium Na + NH 4 Na + Na + Na + Na + Na + Na + Sodium Na +

  25. Cation Exchange Treatment Exposed Ion Exchange General Exchange Process AMMONIUM CATIONS + NH 4 + NH 4 Ra 2+ Radium Ra 2+ Mg 2+ Ca 2+ Barium Ba 2+ Ba 2+ Ra 2+ Schematic Calcium Ca 2+ Cation Mg 2+ Ca 2+ Exchange Resin Bead Magnesium Mg 2+ Na + Ba 2+ + Ammonium NH 4 Na + Na + Na + Na + Na + Na + Sodium Na +

  26. Cation Exchange Treatment Exposed Ion Exchange General Exchange Process MORE HARDNESS CATIONS Mg 2+ Ca 2+ Ra 2+ Radium Ra 2+ Mg 2+ Ca 2+ Barium Ba 2+ Ba 2+ Ra 2+ Schematic Calcium Ca 2+ Cation Mg 2+ Ca 2+ Exchange Resin Bead Magnesium Mg 2+ + NH 4 Ba 2+ + Ammonium NH 4 Na + Na + NH 4 + Na + Na + Na + Sodium Na +

  27. Cation Exchange Treatment Exposed Ion Exchange General Exchange Process REGENERATION Na + Na + Na + Na + Na + Na + Na + Na + Na + Ra 2+ Radium Ra 2+ Na + Na + Na + Na + Mg 2+ Ca 2+ Na + Na + Na + Na + Barium Ba 2+ Ba 2+ Ra 2+ Na + Na + Na + Na + Schematic Calcium Ca 2+ Cation Mg 2+ Ca 2+ Exchange Resin Bead Magnesium Mg 2+ + NH 4 Ba 2+ + Ammonium NH 4 Na + Mg 2+ Ca 2+ Na + Sodium Na +

  28. Cation Exchange Treatment Exposed Ion Exchange WTP Process Flow Schematic Well Fl PO 4 Cl 2 Flow Control No. 1 Valve Bypass Meter Meter Meter Cation Exchange Water Distribution Meter Units System Well No. 2 Meter Sanitary Sewer NaCl System Backwash Surge Regeneration Tank System

  29. Evidence

  30. Evidence  Theory Confirmation No. 1  Village of Montgomery Wells No. 14 & 15 WTP Background  Well No. 14  Ironton Galesville DSS Well  Raw Water Hardness = 235 mg/l as CaCO 3  Combined Radium = 6.6 pCi/l  WTP Contains Five (5) CE Units With Bypass  Flouride, Polyphosphate and Chlorine Gas Added After CE Units  Treated Water Distributed Directly Into System

  31. Evidence  Theory Confirmation No. 1 (Cont.)  Sampling & Testing Summary  Occurred Every 30 Minutes From 8:00 AM – 2:00 PM on April 3, 2013  Testing Locations  Raw Water  Post CE/Pre-Chlorination  Composite  Finished  Tested For Five (5) Test Parameters – Free & Total Ammonia, Chloramine, Free & Total Chlorine  Note: Chlorine Dose = 1.9 mg/l

  32. Evidence Wells No. 14 & 15 WTP Sample Locations Well Raw Fl PO 4 Cl 2 Finished Flow Control No. 14 Meter Valve Bypass Meter Meter Post CE / Well No. 15 Pre ‐ Chlor (Composite) Meter Cation Exchange Units

  33. Evidence Raw Water Ammonia Levels W ELL N O . 14 AND W ELLS N O . 14 & 15 WTP

  34. Evidence Raw & Post CE / Pre-Chlor Ammonia Levels W ELL N O . 14 AND W ELLS N O . 14 & 15 WTP

  35. Evidence Finished Ammonia & Chloramine Levels W ELL N O . 14 AND W ELLS N O . 14 & 15 WTP Mono To Di Mono To Di Near BP

  36. Evidence Finished Ammonia & Chlorine Levels W ELL N O . 14 AND W ELLS N O . 14 & 15 WTP Mono To Di Mono To Di Past BP

  37. Evidence Raw & Finished Ammonia & Chlorine Levels W ELL N O . 14 AND W ELLS N O . 14 & 15 WTP

  38. Evidence Finished Chlorine Residuals W ELL N O . 14 AND W ELLS N O . 14 & 15 WTP

  39. More Evidence

  40. More Evidence  Theory Confirmation No. 2  Village of Montgomery Well No. 8 WTP Background  Well No. 8  Ironton Galesville DSS Well  Raw Water Hardness = 210 mg/l as CaCO 3  Combined Radium = 11.5 pCi/l  WTP Contains Three (3) CE Units With Bypass  Flouride, Polyphosphate and Chlorine Gas Added After CE Units  Treated Water Distributed Directly Into System

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