SlideShare a Scribd company logo
1 of 35
Nanofiltration Membrane
Pilot Studies for
Disinfection By-Product
Control
by Eric Lynne, EIT
 B.S. – Civil and Environmental Engineering
(2007) South Dakota State University
Introduction
 Objective
 Preliminary Tests
 Screening Tests
 Large Scale Pilot Tests
 Conclusions
(Bergantine 2007)
Restrictions
 Stage 2 D/DBP Rule
< 80 μg/L TTHM
< 60 μg/L HAA5
 Big Sioux River
< 1000 mg/L TDS
 Energy Efficient
High Flow at Low Applied Pressure
Background
 DBP Problem
 Treatment Methods:
Chloramination
NF Membranes
 Pilot Plant Testing
Background
 Chloramination
Low DBPs Created
Effective
Background –
Spiral Wound Membrane
(Hydranautics 2008)
1 2 3
4 5
Background
 Membranes
Permeate
Concentrate
Recovery
Stages
(AWWA 1999)
Nanofiltration
Permeate
Concentrate
(AWWA 1999)
Background
 Membrane Problems
Inorganic Scaling
Organic Fouling
Microbial or Silt
Fouling
(Malki 2008, Dow 2008)
Preliminary Testing
 Water Quality
TOC
UV254
SDI
Ammonia
 Chloramination
Preliminary Testing
 Results
Water Quality
• Well Specific
• UV254  TOC
• SDI: Raw < 5; Feed ~ 1
• Naturally occuring ammonia
a) WTP Influent
b) Filter Effluent
Chloramination
0.00
0.50
1.00
1.50
2.00
2.50
3.00
3.50
4.00
0 1 2 3 4 5 6 7 8 9 10 11 12
Chlorine : Ammonia Ratio
Residual(mg/L)
Free Chlorine Total Chlorine
MonoChloramine Free Ammonia
Chloramination
56, 59 μg/L TTHM
Chloramination
0.00
0.50
1.00
1.50
2.00
2.50
3.00
3.50
4.00
0 1 2 3 4 5 6 7 8 9 10 11 12
Chlorine : Ammonia Ratio
Residual(mg/L)
Free Chlorine Total Chlorine
MonoChloramine Free Ammonia
Chloramination
56, 59 μg/L TTHM
10 μg/L TTHM
Preliminary - Conclusions
 Source Water for NF Pilot Plant
 Direct Nanofiltration of raw water is feasible
 Filter Effluent is preferred
 Chloramination
 viable alternative with 82% TTHM reduction
NF Membrane Pilot Plants
 Phase I – Screening
Koch TFC-SR2 (K2)
Koch TFC-SR3 (K3)
Trisep XN45-TSF (T)
Hydranautics ESNA1-LF (HE)
Hydranautics HydraCoRe-70pHT (HH)
Dow/Filmtec NF270 (DF)
(Trisep 2008)
Phase I – Screening
 Hold flux constant
 Vary recovery for each membrane tested
Phase I – Results
 TOC and UV254 removal
NF Membrane and Percent Recovery
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
15 50 80 15 50 80 15 50 80 15 50 80 15 50 80 15 50 80
K2 K3 T HE HH DF
PercentRemoval
TOC UV254
Phase I – Results
 TTHM reduction
NF Membrane and Percent Recovery
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
15 50 80 15 50 80 15 50 80 15 50 80 15 50 80 15 50 80
K2 K3 T HE HH DF
PercentRemoval 87% Minimum Rejection Allowed
Phase I – Results
 Concentrate TDS concentration
0
200
400
600
800
1000
1200
K2 K3 T HE HH DF
NF Membrane
TotalDissolvedSolids(mg/L)
Disposal limit
1000 mg/L
Phase I - Conclusions
Membrane TDS < 1000 mg/L >87% TTHM reduction
Koch TFC-SR2 NO NO
Koch TFC-SR3 NO YES
Trisep XN45-TSF YES YES
Hydranautics ESNA1-LF NO YES
HydraCoRe-70pHT YES NO
Dow/Filmtec NF270 NO YES
Phase II
 85% recovery
 Variable Flux: 9, 12, 15 gfd
 Determine design criteria
Photographs of Pilot Plant
Phase II - Results
 TOC and UV254 removal
50%
55%
60%
65%
70%
75%
80%
85%
90%
95%
100%
9* 12 15 9 12 15 9 12 15
K3 T HE
NF Membrane and Flux Rate (gfd)
PercentRemoval
TOC UV254
50%
55%
60%
65%
70%
75%
80%
85%
90%
95%
100%
9* 12 15 9 12 15 9 12 15
K3 T HE
NF Membrane and Flux Rate (gfd)
PercentReduction
Phase II - Results
 TTHM reduction
87% Minimum
Rejection Allowed
Phase II - Results
 Adjusted Specific Flux
0.00
0.05
0.10
0.15
0.20
0.25
9* 12 15 9 12 15 9 12 15
K3 T HE
NF Membrane and Flux Rate (gfd)
AdjustedSpecificFluxto25°C(gfd/psi)
Phase II - Results
 Ammonia (NH3-N) Removal
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
9* 12 15 9 12 15 9 12 15
K3 T HE
NF Membrane and Flux Rate (gfd)
PercentRejection
Phase II – Results
 Fouling
0
0.05
0.1
0.15
0.2
0.25
0 100 200 300 400 500 600 700 800
Hours
AdjustedSF(gfd/psi).
T HE
Phase II – Results
 Fouling
0
50
100
150
200
250
300
350
400
0 5 10 15 20 25 30
Days
Conductivity(μS/cm)
TriSep XN45-TSF
Hydranautics ESNA1-LF
Phase II - Conclusions

Blend Ratio: 44%/56%
 Concentrate TDS Increased
 SF decreased with increasing flux
 Design Criteria
 Applied pressures ranged from 64-165 psi
 Specific flux values ranged from 0.13-0.21 gfd/psi
 System recovery rate of 85%
 Permeate TTHM values ranging from 1.1-2.5 μg/L
 No substantial fouling observed
Phase II - Conclusions
 Highest Specific Flux = Trisep XN45-TSF
 Highest TTHM rejection = Hydranautics ESNA1-LF
Membrane Optimum Setting Costs
Koch TFC-SR3 __ gfd ??
Trisep XN45-TSF __ gfd ??
Hydranautics ESNA1-LF __ gfd ??
Recommendations
 Cost Data
 Verify 15 gfd @ 80% recovery
 Select Hydranautics ESNA1-LF
15 gfd @ 85% recovery (costs?)
 Consistent Source Water
 One Membrane for Phase II
 Challenge Membrane to Foul
Questions

More Related Content

What's hot

Flow Chemistry Congress Boston 2012 Dh V4
Flow Chemistry Congress Boston 2012 Dh V4Flow Chemistry Congress Boston 2012 Dh V4
Flow Chemistry Congress Boston 2012 Dh V4
dominev
 
Experience In Analysis Bz
Experience In Analysis  BzExperience In Analysis  Bz
Experience In Analysis Bz
binzhao2004
 

What's hot (10)

Flow Chemistry Congress Boston 2012 Dh V4
Flow Chemistry Congress Boston 2012 Dh V4Flow Chemistry Congress Boston 2012 Dh V4
Flow Chemistry Congress Boston 2012 Dh V4
 
journal
journaljournal
journal
 
1448442717.8628chap 4 ce 212
1448442717.8628chap 4 ce 2121448442717.8628chap 4 ce 212
1448442717.8628chap 4 ce 212
 
Gas chromatography in environmental analysis driscoll 2004 l
Gas chromatography in environmental analysis  driscoll  2004 lGas chromatography in environmental analysis  driscoll  2004 l
Gas chromatography in environmental analysis driscoll 2004 l
 
CdTe quantum dots/Poly (diallyl dimethyl ammonium chloride) multilayer films:...
CdTe quantum dots/Poly (diallyl dimethyl ammonium chloride) multilayer films:...CdTe quantum dots/Poly (diallyl dimethyl ammonium chloride) multilayer films:...
CdTe quantum dots/Poly (diallyl dimethyl ammonium chloride) multilayer films:...
 
schuler_imaps_ibm
schuler_imaps_ibmschuler_imaps_ibm
schuler_imaps_ibm
 
Nondestructive Testing at NASA WSTF
Nondestructive Testing at NASA WSTFNondestructive Testing at NASA WSTF
Nondestructive Testing at NASA WSTF
 
80nm Au Carboxyl BioReady for Covalent Conjugations
80nm Au Carboxyl BioReady for Covalent Conjugations80nm Au Carboxyl BioReady for Covalent Conjugations
80nm Au Carboxyl BioReady for Covalent Conjugations
 
NYSAS Seminar LC-IR To Characterize Polymeric Excipients In Pharmaceutical F...
NYSAS Seminar  LC-IR To Characterize Polymeric Excipients In Pharmaceutical F...NYSAS Seminar  LC-IR To Characterize Polymeric Excipients In Pharmaceutical F...
NYSAS Seminar LC-IR To Characterize Polymeric Excipients In Pharmaceutical F...
 
Experience In Analysis Bz
Experience In Analysis  BzExperience In Analysis  Bz
Experience In Analysis Bz
 

Viewers also liked

BBR F-22 EDITED
BBR F-22 EDITEDBBR F-22 EDITED
BBR F-22 EDITED
Brian Bott
 
Ulung furtuna 2 ka17_19113049_proses organisasi 9&10
Ulung furtuna 2 ka17_19113049_proses organisasi 9&10Ulung furtuna 2 ka17_19113049_proses organisasi 9&10
Ulung furtuna 2 ka17_19113049_proses organisasi 9&10
ulungfurtuna
 
Cerasis Presentation_Draft_MarketingPublic
Cerasis Presentation_Draft_MarketingPublicCerasis Presentation_Draft_MarketingPublic
Cerasis Presentation_Draft_MarketingPublic
Adam Robinson
 

Viewers also liked (14)

Andebol
AndebolAndebol
Andebol
 
BBR F-22 EDITED
BBR F-22 EDITEDBBR F-22 EDITED
BBR F-22 EDITED
 
Unit dentar fona nou DenTam Creation
Unit dentar fona nou DenTam CreationUnit dentar fona nou DenTam Creation
Unit dentar fona nou DenTam Creation
 
Vipra today october16
Vipra today october16Vipra today october16
Vipra today october16
 
Factory Beautification
Factory BeautificationFactory Beautification
Factory Beautification
 
Ulung furtuna 2 ka17_19113049_proses organisasi 9&10
Ulung furtuna 2 ka17_19113049_proses organisasi 9&10Ulung furtuna 2 ka17_19113049_proses organisasi 9&10
Ulung furtuna 2 ka17_19113049_proses organisasi 9&10
 
Infographic Base Logistics - EN
Infographic Base Logistics - ENInfographic Base Logistics - EN
Infographic Base Logistics - EN
 
Cerasis Presentation_Draft_MarketingPublic
Cerasis Presentation_Draft_MarketingPublicCerasis Presentation_Draft_MarketingPublic
Cerasis Presentation_Draft_MarketingPublic
 
Gunjan sharma india’s most versatile artist
Gunjan sharma   india’s most versatile artistGunjan sharma   india’s most versatile artist
Gunjan sharma india’s most versatile artist
 
Audience research
Audience researchAudience research
Audience research
 
Uptown Funk
Uptown FunkUptown Funk
Uptown Funk
 
Manjunath_V_CV
Manjunath_V_CVManjunath_V_CV
Manjunath_V_CV
 
Sptpres
SptpresSptpres
Sptpres
 
Media and Democracy
Media and DemocracyMedia and Democracy
Media and Democracy
 

Similar to Defense Presentation 6_26_09

Actiflo Carb + Uf For Nom Removal
Actiflo Carb + Uf For Nom RemovalActiflo Carb + Uf For Nom Removal
Actiflo Carb + Uf For Nom Removal
guest10a8db
 
Research Background
Research BackgroundResearch Background
Research Background
Brian Wisner
 

Similar to Defense Presentation 6_26_09 (20)

Actiflo Carb + Uf For Nom Removal
Actiflo Carb + Uf For Nom RemovalActiflo Carb + Uf For Nom Removal
Actiflo Carb + Uf For Nom Removal
 
Operation & Maintenance WTP.pptx
Operation & Maintenance WTP.pptxOperation & Maintenance WTP.pptx
Operation & Maintenance WTP.pptx
 
Membrana training
Membrana trainingMembrana training
Membrana training
 
Prez Baljaa09
Prez Baljaa09Prez Baljaa09
Prez Baljaa09
 
Optimization of Tangential Flow Filtration Applications and Scale Up Consider...
Optimization of Tangential Flow Filtration Applications and Scale Up Consider...Optimization of Tangential Flow Filtration Applications and Scale Up Consider...
Optimization of Tangential Flow Filtration Applications and Scale Up Consider...
 
Optimization of Tangential Flow Filtration Applications and Scale Up Consider...
Optimization of Tangential Flow Filtration Applications and Scale Up Consider...Optimization of Tangential Flow Filtration Applications and Scale Up Consider...
Optimization of Tangential Flow Filtration Applications and Scale Up Consider...
 
Wett and Puempel DEMON technology
Wett and Puempel DEMON technologyWett and Puempel DEMON technology
Wett and Puempel DEMON technology
 
Research Background
Research BackgroundResearch Background
Research Background
 
Atomic Layer Deposition: a process technology for transparent conducting oxides
Atomic Layer Deposition: a process technology for transparent conducting oxidesAtomic Layer Deposition: a process technology for transparent conducting oxides
Atomic Layer Deposition: a process technology for transparent conducting oxides
 
General Presentation Uf
General Presentation   UfGeneral Presentation   Uf
General Presentation Uf
 
C&I Cables Tests
C&I Cables TestsC&I Cables Tests
C&I Cables Tests
 
C&I Cables Tests
C&I Cables TestsC&I Cables Tests
C&I Cables Tests
 
METHOD DEVELOPMENT AND VALIDATION FOR DETERMINATION OF HUMAN SERUM ALBUMIN MO...
METHOD DEVELOPMENT AND VALIDATION FOR DETERMINATION OF HUMAN SERUM ALBUMIN MO...METHOD DEVELOPMENT AND VALIDATION FOR DETERMINATION OF HUMAN SERUM ALBUMIN MO...
METHOD DEVELOPMENT AND VALIDATION FOR DETERMINATION OF HUMAN SERUM ALBUMIN MO...
 
325 steevn
325 steevn325 steevn
325 steevn
 
High Flow Filter for UPW Applications – A Field Case Study
High Flow Filter for UPW Applications – A Field Case StudyHigh Flow Filter for UPW Applications – A Field Case Study
High Flow Filter for UPW Applications – A Field Case Study
 
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
 
Introduction to Tangential Flow Filtration (TFF)
Introduction to Tangential Flow Filtration (TFF)Introduction to Tangential Flow Filtration (TFF)
Introduction to Tangential Flow Filtration (TFF)
 
Introduction to Tangential Flow Filtration (TFF)
Introduction to Tangential Flow Filtration (TFF)Introduction to Tangential Flow Filtration (TFF)
Introduction to Tangential Flow Filtration (TFF)
 
Circulating water treatment project
Circulating water treatment projectCirculating water treatment project
Circulating water treatment project
 
Presentation given at SKYREC seminar, 2011
Presentation given at SKYREC seminar, 2011Presentation given at SKYREC seminar, 2011
Presentation given at SKYREC seminar, 2011
 

Defense Presentation 6_26_09

  • 1. Nanofiltration Membrane Pilot Studies for Disinfection By-Product Control by Eric Lynne, EIT  B.S. – Civil and Environmental Engineering (2007) South Dakota State University
  • 2. Introduction  Objective  Preliminary Tests  Screening Tests  Large Scale Pilot Tests  Conclusions
  • 4. Restrictions  Stage 2 D/DBP Rule < 80 μg/L TTHM < 60 μg/L HAA5  Big Sioux River < 1000 mg/L TDS  Energy Efficient High Flow at Low Applied Pressure
  • 5. Background  DBP Problem  Treatment Methods: Chloramination NF Membranes  Pilot Plant Testing
  • 7. Background – Spiral Wound Membrane (Hydranautics 2008) 1 2 3 4 5
  • 10. Background  Membrane Problems Inorganic Scaling Organic Fouling Microbial or Silt Fouling (Malki 2008, Dow 2008)
  • 11. Preliminary Testing  Water Quality TOC UV254 SDI Ammonia  Chloramination
  • 12. Preliminary Testing  Results Water Quality • Well Specific • UV254  TOC • SDI: Raw < 5; Feed ~ 1 • Naturally occuring ammonia a) WTP Influent b) Filter Effluent
  • 13. Chloramination 0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 0 1 2 3 4 5 6 7 8 9 10 11 12 Chlorine : Ammonia Ratio Residual(mg/L) Free Chlorine Total Chlorine MonoChloramine Free Ammonia
  • 15. Chloramination 0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 0 1 2 3 4 5 6 7 8 9 10 11 12 Chlorine : Ammonia Ratio Residual(mg/L) Free Chlorine Total Chlorine MonoChloramine Free Ammonia
  • 16. Chloramination 56, 59 μg/L TTHM 10 μg/L TTHM
  • 17. Preliminary - Conclusions  Source Water for NF Pilot Plant  Direct Nanofiltration of raw water is feasible  Filter Effluent is preferred  Chloramination  viable alternative with 82% TTHM reduction
  • 18. NF Membrane Pilot Plants  Phase I – Screening Koch TFC-SR2 (K2) Koch TFC-SR3 (K3) Trisep XN45-TSF (T) Hydranautics ESNA1-LF (HE) Hydranautics HydraCoRe-70pHT (HH) Dow/Filmtec NF270 (DF) (Trisep 2008)
  • 19. Phase I – Screening  Hold flux constant  Vary recovery for each membrane tested
  • 20. Phase I – Results  TOC and UV254 removal NF Membrane and Percent Recovery 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% 15 50 80 15 50 80 15 50 80 15 50 80 15 50 80 15 50 80 K2 K3 T HE HH DF PercentRemoval TOC UV254
  • 21. Phase I – Results  TTHM reduction NF Membrane and Percent Recovery 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% 15 50 80 15 50 80 15 50 80 15 50 80 15 50 80 15 50 80 K2 K3 T HE HH DF PercentRemoval 87% Minimum Rejection Allowed
  • 22. Phase I – Results  Concentrate TDS concentration 0 200 400 600 800 1000 1200 K2 K3 T HE HH DF NF Membrane TotalDissolvedSolids(mg/L) Disposal limit 1000 mg/L
  • 23. Phase I - Conclusions Membrane TDS < 1000 mg/L >87% TTHM reduction Koch TFC-SR2 NO NO Koch TFC-SR3 NO YES Trisep XN45-TSF YES YES Hydranautics ESNA1-LF NO YES HydraCoRe-70pHT YES NO Dow/Filmtec NF270 NO YES
  • 24. Phase II  85% recovery  Variable Flux: 9, 12, 15 gfd  Determine design criteria
  • 26. Phase II - Results  TOC and UV254 removal 50% 55% 60% 65% 70% 75% 80% 85% 90% 95% 100% 9* 12 15 9 12 15 9 12 15 K3 T HE NF Membrane and Flux Rate (gfd) PercentRemoval TOC UV254
  • 27. 50% 55% 60% 65% 70% 75% 80% 85% 90% 95% 100% 9* 12 15 9 12 15 9 12 15 K3 T HE NF Membrane and Flux Rate (gfd) PercentReduction Phase II - Results  TTHM reduction 87% Minimum Rejection Allowed
  • 28. Phase II - Results  Adjusted Specific Flux 0.00 0.05 0.10 0.15 0.20 0.25 9* 12 15 9 12 15 9 12 15 K3 T HE NF Membrane and Flux Rate (gfd) AdjustedSpecificFluxto25°C(gfd/psi)
  • 29. Phase II - Results  Ammonia (NH3-N) Removal 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% 9* 12 15 9 12 15 9 12 15 K3 T HE NF Membrane and Flux Rate (gfd) PercentRejection
  • 30. Phase II – Results  Fouling 0 0.05 0.1 0.15 0.2 0.25 0 100 200 300 400 500 600 700 800 Hours AdjustedSF(gfd/psi). T HE
  • 31. Phase II – Results  Fouling 0 50 100 150 200 250 300 350 400 0 5 10 15 20 25 30 Days Conductivity(μS/cm) TriSep XN45-TSF Hydranautics ESNA1-LF
  • 32. Phase II - Conclusions  Blend Ratio: 44%/56%  Concentrate TDS Increased  SF decreased with increasing flux  Design Criteria  Applied pressures ranged from 64-165 psi  Specific flux values ranged from 0.13-0.21 gfd/psi  System recovery rate of 85%  Permeate TTHM values ranging from 1.1-2.5 μg/L  No substantial fouling observed
  • 33. Phase II - Conclusions  Highest Specific Flux = Trisep XN45-TSF  Highest TTHM rejection = Hydranautics ESNA1-LF Membrane Optimum Setting Costs Koch TFC-SR3 __ gfd ?? Trisep XN45-TSF __ gfd ?? Hydranautics ESNA1-LF __ gfd ??
  • 34. Recommendations  Cost Data  Verify 15 gfd @ 80% recovery  Select Hydranautics ESNA1-LF 15 gfd @ 85% recovery (costs?)  Consistent Source Water  One Membrane for Phase II  Challenge Membrane to Foul

Editor's Notes

  1. Name, graduated in 07 with BS in CEE getting MS in engineering, civil and environmental engineering, emphasis on w/ww treatment will be working in Sheboygan WI at Donohue and Associates as a ww process engineer
  2. Briefly state: will go in this order
  3. Objective was determined using the following restrictions applied to NF
  4. insert picture of random pilot DBP’s are a carcinogen, some form when free chlorine oxidizes NOM, the max potential TTHM is 120 micrograms/L, reduce using treatment Note chloramination briefly, membranes – spiral wound style Tighter like RO Pilot plant verification
  5. insert image of laboratory testing Free Chlorine reacts with NOM, avoid this by using a different disinfectant Chloramination uses ammonia to combine with free chlorine to create a less reactive disinfectant for DBP control Note how Chloramines not desired, expansion, remove problem physically
  6. Define Terms using picture (add another picture(s) with membrane diagram from Hydranautics video)
  7. Define Terms using pictures (Add image for antiscalant) Address scaling problem (antiscalant) Fouling reduced using proper cross flow Operation settings are vital to efficient use, determined in pilot tests Microbial and silt/collodial fouling are possible, but were not a problem in this study
  8. overview
  9. Water Quality (conductivity, alk, hardness) typical of ground water obtained from BS aquifer however, compared to Brookings TOC contributes to (UV/TOC images, SDI images)
  10. Insert theory image then overlay experimental results As predicted, breakpoint chlorination far right, chloramination operate 4:1 area
  11. Insert theory image then overlay experimental results As predicted, breakpoint chlorination far right, chloramination operate 4:1 area
  12. Insert theory image then overlay experimental results As predicted, breakpoint chlorination far right, chloramination operate 4:1 area
  13. Insert theory image then overlay experimental results As predicted, breakpoint chlorination far right, chloramination operate 4:1 area
  14. Based on SDI values and literature Repeat values to support statement
  15. Add image of membrane
  16. Add 2 images of Phase I pilot
  17. TOC removal limits formation of DBPs Note percent reduction not an absolute permeate value, depends on the feed water
  18. TTHM trends with the TOC/UV removals, higher = higher, but trade off is that they have also exhibit high TDS HAA5 removal is not a concern for WMU, considerable reductions of HAA5 do occur and vary with membrane and settings
  19. TDS to river
  20. Discuss reasons and compromises Trisep covered both Not df due to similarity to k3 but k3 was already delivered (koch provided the skid for phase II testing) NEEDED THM reduction, TDS requirement was just re-evaluated by the SDDENR – soon to increase to 2500 mg/L
  21. Describe the unit some more (21 elements) After flux test, perform fouling test
  22. Operated for a week, rather than few hours at each setting
  23. All membranes are able to achieve minimum (T at 9 doesn’t)
  24. Higher number is better, less electricity Higher TOC/TTHM removal relates to lower SF values
  25. No removal required, but higher values of removal are desired to save chemical costs of chlorine during breakpoint chlorination
  26. No significant evidence of fouling (typically 15% reduction in SF indicates time to initiate a chemical cleaning)
  27. No significant fouling, conductivity should decrease if fouling is building up and blocking pores
  28. Blend of 44perm, 56 softened (used to establish the 87% removal criteria, if lowered would cost more to NF treat more) TDS increased due to 85% recovery setting SF decr with incr flux for all membranes Perm TTHM values 1-2 to be blended with bypassed filter effluent
  29. TDS due to 85% recovery setting Optimum Setting of 15 gfd based on 87% TTHM satisfaction. Although the SF may decrease (depends on energy costs) fewer elements, piping, floor space will be required. Best TTHM removal not required, just desired (as long as 87% then ok)