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Reverse Osmosis
Dam
Pumping
Raw Water
Treatment Plant
Pumping
Wastewater
Treatment Plant
Collection Network
Rain
Agricultural Use
IncinerationSludge Treatment
Plant
Collection
Water Cycle
Distribution
Network
Boiler
Cooling Tower
Process
Discharge
Water Cycle
• Dramatic decrease in RO membrane prices (50% - 8yrs).
• Increasing costs of chemicals (esp. NaOH) for IX systems.
• Increased return on investment for reverse osmosis as pretreatment
to an ion-exchange system.
• Increased manufacturer awareness in properly designing
pretreatment systems.
• Increase in comfort level for operation of customer-owned RO
systems.
• Consistent water quality
REASONS FOR INCREASED POPULARITY WITH
REVERSE OSMOSIS
RO Seminar Objectives
– Reverse Osmosis Principles and Operation
(Reverse Osmotic Pressure)
– Designs and terminology
– Operating parameters, problems, troubleshooting
– Cleaning
– Products and Equipment
– Miscellaneous subjects
Reverse Osmosis
Basic Principles
Osmosis
Pure
Water
Strong
Solution
H2O
H2O
H2O
Pure Water Flow
Osmosis
Osmotic Head
Pure
Water
Strong
Solution
H2O
H2O
H2O
Pure Water Flow
Equilibrium
Equilibrium
Applied Pressure, PF
H2O
H2O
H2O
Strong
Solution
Pure
Water
= Osmotic Pressure, POF
Osmotic Pressure, PO,P
Reverse Osmosis
Applied Pressure, PF > Permeate Pressure, PP
H2O
H2O
H2O
Strong
Solution
Pure Water Flow
Pure
Water
Osmotic
Pressure, PO,F
Osmotic Pressure, PO,P
Types of Filtration
TYPICAL
FILTRATION
CROSS-FLOW
FILTRATION
Solids on surface quickly
foul the membrane
Solids are swept away
by continuous flow
Feedwater FlowFeedwater
Flow
Purified waterPurified water
CROSS-FLOW FILTRATION
CROSS-FLOW
FILTRATION
•ONE INFLUENT
•TWO EFFLUENT STREAMS
•HIGH VELOCITY MINIMIZES MEMBRANE
SCALING AND FOULING
RO Skids typically have three major
components.
TO WASTE
PRODUCTFEED
CARTRIDGE
FILTER HIGH-PRESSURE
FEED PUMP
PRESSURE
VESSELS
REVERSE OSMOSIS
Cross Flow Filtration Methods
Microfiltration Ultrafiltration Nanofiltration Reverse
Osmosis
Range Macro molecular Molecular Sub molecular Ionic
Particle
size
1.0 - 0.1
Micron
0.1 - 0.01
Micron
0.01 - 0.001
Micron
<0.001
Micron
Removes Suspended solids,
Large colloids,
Bacteria
Proteins,
Colloids,
Organics
Pyrogens,
Divalent ions
Virus
Small Organics,
Metals,
Salts
Molecular
Weight
>100,000 10,000 - 100,000 200 - 20,000 <300
Operating
Pressure
10 psig
(0.7 kg/cm2)
10 - 100 psig
(0.7 kg-7.0/cm2)
150 -250 psig
(14-17.5 kg/cm2)
150 - 800 psig
(14- 56 kg/cm2)
Pretreatment
Needs
Low Medium High High
Capital Cost Low Medium High High
The Filtration Spectrum
Thin Film Composite Polyamide Membrane
0.2 micron
40 micron
120 micron
Reinforcing
Fabric
Microporous
Polysulfone
Polyamide
Ultrathin
Barrier Layer
TFC Membrane
Membrane Comparison
Characteristic TFCCA
Operating pH 2 - 11
Salt Rejection >99%
Flux Rate (GPD/Ft2) 15-20
Bacteria Resistance Excellent
Cl2 Tolerance 0.0
Physical Stability Better
Max T (0F) 113
Feed Pressure
5 - 6.5
90-96%
12-16
Poor
0.2-1.0
Good
104
> 400 PSI < 200 PSI
Membrane Comparison Cont.
CA TFC
Silica Rejection 85% 98%
Nitrate Rejection 85% 94%
Maximum SDI 5 5
3rd Year Compaction 20% 0%
Hydrolysis 2 X None
Characteristic
Typical Passage of Ions
IonIon %% SaltSalt PassagePassage % Salt Rejection% Salt Rejection
AmmoniumAmmonium 55 9595
SodiumSodium 22 9898
PotassiumPotassium 22 9898
MagnesiumMagnesium <1<1 99+99+
StrontiumStrontium <1<1 99+99+
CalciumCalcium <1<1 99+99+
NitrateNitrate 1515 8585
BisilicateBisilicate 1010 9090
ChlorideChloride 22 9898
FluorideFluoride 22 9898
BicarbonateBicarbonate 22 9898
SulfateSulfate 11 9999
PhosphatePhosphate 11 9999
* TFC element rated for a 98%* TFC element rated for a 98% NaClNaCl rejectionrejection
Membrane Configurations
• Spiral Wound
• Hollow Fiber
• Tubular
Spiral Wound Membrane Elements
Flow
Pattern
for a
Spiral
Wound
Element
Spiral Wound Membrane Elements
Wound Elements
Hollow Fiber Membrane
Hollow Fiber Membrane Element
Feedwater
P
e
r
m
e
a
t
e
Concentrate
Concentrate
Note: Only 4 hollow fibers are shown
Tubular Membrane
Reverse Osmosis
System Design & Operations
Glossary of Terms
• Concentrate
– Reject
– Brine
• Permeate
– Product
Reverse Osmosis Basics
FEEDWATER
100 gpm
600 ppm TDS
PERMEATE
75 gpm
30 ppm TDS
5% Salt Passage
75% Recovery
CONCENTRATE
95% Salt Rejection
25 gpm
2310 ppm TDS
25% Concentrate
What is RO Permeate and % Recovery?
• Permeate is water recovered as product.
• % Recovery = Permeate Flow Rate x100
– % Recovery calculates percent of feedwater that
becomes product.
– % Recovery describes performance of the system
– Greater recovery=less waste=cost savings.
– Recovery typically ranges from 50% to 75% (can go
as high as 85%)
– % Recovery and permeate quality are inversely
related.
REVERSE OSMOSIS
Make-up Flow Rate
REVERSE OSMOSIS
RECOVERY CONCENTRATION
FACTOR
50% 2
75% 4
80% 5
83% 6
87.5% 8
What is RO Concentrate and % Rejection?
• Concentrate (or Brine) is the waste from the RO.
• Reject is a calculation of the percentage of
solids/solutes in feedwater rejected by the
membrane.
– Typically ranges from 95% to 99+% for most ionic
solutes and set by membrane manufacturer.
– Greater % reject means better permeate quality.
– Species dependant
• Multi-valent ions (Ca2+, Mg2+) higher rejection
• Monovalent ions (Na+, Cl-) lower rejection
• Gases (O2, CO2) no rejection
REVERSE OSMOSIS
RO Systems
– Reject Staging
• Multi-stages for reject
• Increased utilization of water
– Incremental increase in investment
– Minimal decrease in water quality
– Multi - Pass
• Product staging
• Improves water quality
– May eliminate the need for downstream
polishing
Two-Stage RO System - Reject Staging
FEEDFEED PERMEATEPERMEATE
HIGHHIGH
PRESSUREPRESSURE PUMP
TRAIN #1TRAIN #1
TRAIN #2TRAIN #2
ELEMENTSELEMENTS
VESSELVESSEL
2:1 ARRAY2:1 ARRAY
FEEDFEED
REJECTREJECT
CONCENTRATECONCENTRATE
PERMEATEPERMEATE
1st STAGE1st STAGE
2nd STAGE2nd STAGE
CONCENTRATECONCENTRATE
Reject Staging
• Increased Utilization of
Water
– Incremental Increase in
Investment
– Minimal Degradation in
Water Quality
Double Pass RO System
2nd Pass Concentrate Recycled
* pH 9.0* pH 9.0
w/w/ NaOHNaOH
PermeatePermeate
FeedFeed
1st Pass Permeate
11 stst Pass Concentrate to Drain
Double Pass
• Applications:
– Seawater (High TDS)
– Ultra-high purity applications
• Benefits of interstage pH
adjustment
– Improved Alkalinity Rejection
– Improved Silica Rejection
– Improved TOC Rejection
Typical RO Machine
What Are the Advantages of RO ?
• Removes nonionic impurities and dissolved solids
(i.e. organics, silica, bacteria)
• Reduction of hazardous chemical storage and
handling associated with ion exchange
• Economic advantages increase with increasing
feed TDS
What Are the Disadvantages of RO?
• Concentrate is rejected and this can be a significant volume of
water.
• RO membranes reject a fixed percentage of feedwater ions
– Further treatment is required for many applications.
• Ultimate filter which is easily fouled:
– Increasing operating costs
– Reducing membrane life
Typical Operating Cost Breakdown
Membrane
Replacement
12%
Chemicals
14%
Labor
25%
Other
5%
Electrical
44%
Reverse Osmosis
Membrane Problems and Solutions
Membrane Problems
 Scaling
- Mineral Salts
- Silica
 Fouling
- Metal Oxides
- Colloidal Silt & Crud
- Biological & Organics
 Hydrolysis & Chemical Attack
- pH, Temperature, Oxidants, Biodegradation
 Compaction
REVERSE OSMOSIS
•80% to 90% of problems are
related to pretreatment of RO
Feedwater
•The purpose of pretreatment is
to prevent
• Membrane Fouling
• Membrane Scaling
• Membrane Degradation
REVERSE OSMOSIS
Effects of Fouling, Scale, Degradation
Poor Permeate Quality
Frequent cleaning
Increased Operating Pressure
Increased O&M cost
Membrane Replacement
RO Fouling
CategoryCategory ExamplesExamples SourcesSources
Scaling SaltsScaling Salts CaCOCaCO33 FeedwaterFeedwater
CaSOCaSO44 Sulfuric AcidSulfuric Acid
BaBa // SrSr -- SOSO44
CaFCaF22
SiOSiO22 -- ComplexesComplexes
Metal OxidesMetal Oxides IronIron FeedwaterFeedwater
ManganeseManganese CorrosionCorrosion
AluminumAluminum ClarifiersClarifiers
ColloidsColloids SiltSilt Surface WatersSurface Waters
RustRust Corroding PipesCorroding Pipes
BiologicalBiological Organic SlimesOrganic Slimes NonNon--ClCl22 FeedFeed
BacteriaBacteria OffOff--line Systemsline Systems
OrganicOrganic PolymerPolymer Coagulant OverfeedCoagulant Overfeed
HydrocarbonHydrocarbon Process LeaksProcess Leaks
Scale
• Cause:
– Salt exceeds solubility limits due to
concentration effects
• Prevention:
– Reduce Recovery
– Acid Feed (CaCO3)
– Sodium Zeolite Softening
– Antiscalant
Concentration Polarization
Mineral Scale
Silica Fouling
Metal Oxide
Iron, Manganese and Aluminum
• Cause:
– Feedwater
– Corrosion in system piping
– Clarifier carryover
• Prevention:
– Oxidation & Filtration
– Greensand Filtration (Mn)
– Softening (Fe & Mn)
– Chemical Antifoulant
Iron Fouling
REVERSE OSMOSIS
•RO
For:
• DOSAGE CONTROL
• LEAK ANALYSIS DIAGNOSTICS
• TRUE SYSTEM RECOVERY
• MEMBRANE INTEGRITY
• COST CONTROL
SCALE CONTROL
Components of RO TRASAR®
Trasar 8000 Handheld Fluorometer
for Monitoring and Diagnostics
Trasar 3000 Fluorometer for
On-line Monitor & Control
120 MW CCGT Cogeneration
Plant, Florida
• Description of demineralization system
– Water source: city water
– Pre-treatment: feed water dechlorination
– Reverse osmosis: 2X100 gpm systems
– Post-treatment: mixed-bed ion exchange column
• Performance issues
– Fouling of membrane elements resulting in frequent
cleanings
– Poor permeate quality resulting in frequent regeneration of
polishing ion exchange bed.
Active control of
scale inhibitor dosage
0
5
10
15
20
25
30
0
50
100
150
200
250
Hours of Continuous Operation
PPMasAntiscalant
Before Control After Control
Reduced membrane fouling.
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
160
180
200
Hours of Continuous Operation
ppmantiscalant
Actual Dose
Target Dose & Control
Limits
RO TRASAR® Benefits: 120 MW
CCGT Cogeneration Plant
> $37,600/yrTotal Savings
TBD88%Every 800K galEvery 100K galPolishing IX
regeneration
$6,00050%4 yrs life2 yr lifeMembrane
replacement
$26,00085%4 per year26 per yearCleaning
$5,60025%9 ppm12 ppmAntiscalant
$/yr%AfterBefore
Savings
Colloids
• Cause:
– Surface water
– Corrosion in system piping - (Line
all vessels)
• Prevention:
– Coagulation & filtration
– Zeolite softening
– Chemical Antifoulant
Bacteria, Slime
• Cause:
– Surface water
– Non-Cl2 Feed
– Off-Line RO System
• Prevention:
– Biocide
• Cl2 residual
– Dechlorination
• Non-Oxidizing Biocide
• UV Sterilization
Microbiological Fouling
Organic
• Cause:
– Polymer overfeed
– Surface Water
– Process Leaks
• Prevention for Polymer Overfeed:
– Streaming Current Detector
– Sodium Zeolite Softener
– Inorganic Coagulant
Hydrolysis & Chemical Attack
CA MEMBRANES
• Microbio growth present
• pH < 5.0 or > 6.5
• Temperatures > 104 oF (40 0C)
• Exposed to direct sunlight
TFC MEMBRANES
• Oxidants in feedwater
(i.e. Cl2, O3)
• Temperatures > 112 oF (44 0C)
• Exposed to direct sunlight
Membrane Degradation
Results of Membrane Problems
• Reduced water quality
– Shorter run lengths on downstream IX
• Premature membrane replacement
• Higher operating costs
Reverse Osmosis
Monitoring
Monitoring
• Pretreatment
– 90% of operational
problems are found here
• System
– 10% of operational
problems are found here
RO System Monitoring
• Pretreatment monitoring
- Silt Density (SDI), Turbidity, pH,
Oxidants Particle Size and Counts
- Temperature, Pressure, TDS
- Foulants (bacteria, metals,
hardness, silica)
RO System Monitoring
• Performance monitoring
- Percent salt rejection
- Normalized permeate flowrate
- Differential pressure
Pretreatment
• Silt Density Index (SDI)
• Langlier Saturation Index (LSI)
• Stiff Davis Index (TDS >4,000 mg/L)
• Feedwater Analysis
Silt Density Index (SDI)
• Empirical indication of potential fouling
• Based on rate of plugging a 0.45m filter
• Hollow Fiber SDI < 3.0
• Spiral Wound SDI < 5.0
• Typical Well Water SDI < 3
• Typical Surface Water SDI > 6
Silt Density Index
SDI = PSDI = P3030 // T = (1T = (1 -- ttii // ttff) * 100) * 100
TT
SDI = PSDI = P3030 // T = (1T = (1 -- ttii // ttff) * 100) * 100
TT
FeedFeed
SupplySupply
(30(30--8080
psig)psig)
PressurePressure
RegulatorRegulator
PressurePressure
GaugeGauge
ByBy--Pass toPass to
draindrain
FilterFilter
HolderHolder
FilterFilter
HolderHolder
Langlier Saturation Index (LSI)
• Indicates the potential for CaCO3
scale
• LSI > 0 “indicates scaling”
• Calculation:
– Computer programs
– Permutit Handbook
REVERSE OSMOSIS
PERMACARE RO-12
SCALE PREDICTION SOFTWARE
Feedwater Analysis
• Minimal water test includes
– Ca, Mg, Fe, Al, Silica
– SO4, Alkalinity, pH, Conductivity
– SDI
– TOC
– Color
• Full water analysis should include
analysis scaling/fouling contaminants
Additional Pretreatment
• Turbidity
• pH
• Oxidants
• Temperature
• Pressure
• TDS / Conductivity
• Foulants - bacteria, metals, hardness, silica
etc.
Affect of SDI on Flux & % Recovery per
Element
Feed source SDI
Max. Flux
(gal/ft2/day)
Max. %
Recovery
RO permeate <1 25 30%
Well water <3 20 19%
Surface supply <3 17 17%
Surface/softened <5 16 15%
Seawater <5 10 13%
Guidelines for 8 inch
Filmtec element
Affect of SDI on Flux by System
Feed source SDI
Max. Flux
(gal/ft2/day)
RO permeate <1 21 – 25
Well water <3 16 – 20
Surface supply <3 13 – 17
Surface supply <5 10 – 16
Nalco recommendations
for longer membrane life
Nalco
Recommendation
22
16
14
13
Effect of Temperature on Permeate Flowrate
TEMPERATURETEMPERATURE
--1.11.1 4.44.4 10.010.0 15.615.6 21.121.1 26.726.7 32.232.2 37.837.8 43.343.3
PermeateFlowrate,PermeateFlowrate,
%ofDesign%ofDesign
7070
8080
9090
100100
110110
6060
4040 5050 6060 7070 8080 9090
120120
1001003030 110110 00
FF
00
CC
System Monitoring
The Critical 3
• Percent Salt Rejection
• Normalized Permeate Flowrate (NPF)
• Differential Pressure (ΔP)
(Use Computer and Trend Data)
Salt Rejection
% Rejection = (TDSfeed - TDSPermeate) x 100
TDSfeed
Common to use conductivity measurement as an
indication of TDS
Net Differential Pressure
DP = Pf - Pc
Pf = feed pressure
Pc = concentrate pressure
DP differential pressure, “delta P” or pressure drop
Normalized Permeate Flowrate
Flownormalize : Qn = NDP(start-up) * FT * Qp
NDP(daily)
Pf = Feed Pressure
Pp = Permeate Pressure
PO,F = Osmotic Press. Feed
PO,C = Osmotic Press. Brine
FT = Temp. Correction
Factor
Qp = Permeate Flowrate
NDP = Pf - Pp - PO
NDP = Pf - Pp - PO
Net Driving Pressure
Available Pressure to “Drive” the Process
• NDP = PF + PO,P - PP - PO,F
• Brackish water PO,P = 0
• Average NDP
• NDP = PF - PP - PO,F
• NDP = (PF+Pc) - (PP+PP) - (PO,F+PO,C)
2 2 2
Trending & Normalization
• Permeate Flow
• Differential
Pressure
• Salt Rejection
Enter Data Using Nalco “RO Trend”
Effect of Driving Pressure on Permeate FlowratePermeateFlowrate,%PermeateFlowrate,%
PercentRejection,%PercentRejection,%
20%20%
40%40%
60%60%
80%80%
100%100%
0%0%
20%20% 40%40% 60%60% 80%80% 100%100% 120%120%
20%20%
40%40%
60%60%
80%80%
100%100%
0%0%
DRIVING PRESSUREDRIVING PRESSURE
Feed Flow Vs. NDP
Raw Data Vs. Normalized Data
Start Up Information
• Collect Initial Data within first 24 to 72 hours
• Everything is compared to “Start up” data
Daily Operation & Performance Parameters
Date
Operator’s initials
Feedwater silt density index (SDI)
Feedwater turbidity
Feedwater temperature
Feedwater temperature correction
factor
Feedwater pH
Oxidant concentration (i.e. Cl, sanitizer)
Feedwater conductivity or TDS
Permeate conductivity or TDS
Reject conductivity or TDS
Percent salt rejection (calculated)
Feed (membrane) pressure
Permeate pressure
Reject pressure
Net differential pressure (calculated)
Net driving pressure
Feedwater flowrate
Permeate flowrate
Reject flowrate
Normalized permeate flowrate
(calculated)
Percent recovery (calculated)
Use Computers to Trend this Data
Trending Data
Using the Performance Variable
Feed Flow
Rate (gpm)
120
110
100
90
100
90
80
100
90
80
40
30
20
Differential Pressure
Feed Flow Rate
Start-up
Membrane Elements
cleaned
Leaking O-ring
Replaced
Net Differential
Pressure
(psig)
%
Reject
Normalized
Permeate
Flow Rate
(gpm)
REVERSE OSMOSIS
•RO-EYE
• REVERSE OSMOSIS
MONTIROING AND
CONTROL SYSTEM
• Real time data monitoring
• Data normalization
• TRASAR control
T
M
Reverse Osmosis
Trouble Shooting
Product
ConcentrateFeed
Brine becomes more concentrated
Feed Flowrate Decreases
Flow Through a Pressure Vessel
Indications of Trouble
Change
• Salt Rejection
• Differential Pressure
• Normalized Permeate Flow
• Others
Trouble Shooting Changes
• Check Instrument Calibrations
– Compare Percent Recovery by Conductivity Vs.
Flow
• Identify the Location of the Decline
– Front end Vs. Back end, Stage 1 Vs. Stage 2
• Investigate Potential Causes of the Problem
– Use both visual and analytical data
• Correct the Potential Cause of the Problem
Troubleshooting
Instrument Calibration
• Compare Recovery Calculations
– Conductivity Vs. Flow
• Pressure Meter Change Out
– Quick Disconnects
• Hand Held Vs. On-line Instrumentation
• Thermometers
Trouble Shooting / Changes in Salt Rejection
• Check Individual Pressure Vessel
Performance
• Probe the Pressure Vessel (Spiral
Wound)
• Individual Membrane Testing
– Single Element Test Skid
Identify the Location of the Decline
Check Individual Pressure Vessel Performance
First Stage Pressure Vessel Profile:
Pressure Vessel # Permeate TDS (ppm)
1 25
2 22
3 49
4 20
Second Stage Pressure Vessel Profile:
5 36
6 34
Example - 4:2 Array
When to Probe
• High salt passage
• Individual pressure vessels have
high conductivity
Individual Element Performance
• Probe the Pressure Vessel (Spiral Wound)
– 1/4” Tubing into Permeate Line
– Conductivity versus Penetration
• Location of Problem
– Check front / mid / end each element
– Note direction of feed water flow
1/4”
Polypropylene
Tubing
RO Vessel Containing 6 Elements
Probing a Pressure Vessel
Probe every 8 inches to determine membrane or o-ring damage
Membrane Element # Permeate TDS (ppm)
1 Lead End 25
2 23
3 25
4 21
5 Tail End 54
Probing a Pressure Vessel
Remember to Note Feedwater Direction
Troubleshooting Individual Membrane Elements
• Individual Membrane Testing
– In House
• Non-destructive
– Single Element Test Stand
– Autopsy
• Potentially Destructive
• More detailed Information`
Problems
CauseCause General SymptomsGeneral Symptoms
Salt PassageSalt Passage PermeatorPermeator DD PP Product FlowProduct Flow
ScalantsScalants
Carbonates, Sulfates,Carbonates, Sulfates,
PhosphatesPhosphates
SignificantSignificant
Increase (10Increase (10--25%)25%)
Slight to ModerateSlight to Moderate
IncreaseIncrease
(10(10 -- 50%)50%)
Slight DecreaseSlight Decrease
(( << 10%)10%)
Metal OxidesMetal Oxides
FoulantsFoulants
Iron, Manganese etc.Iron, Manganese etc.
Rapid MarkedRapid Marked
Increase (Increase ( >> 2x)2x)
Rapid MarkedRapid Marked
Increase (Increase ( >> 2x)2x)
Rapid MarkedRapid Marked
Decrease (Decrease ( >> 50%)50%)
ColloidalColloidal GradualGradual GradualGradual GradualGradual
FoulantsFoulants
mostly Aluminum Silicatesmostly Aluminum Silicates
Marked IncreaseMarked Increase
(( >> 2x)2x)
Marked IncreaseMarked Increase
(( >> 2x)2x)
Marked DecreaseMarked Decrease
(( >> 50%)50%)
BiofilmBiofilm
FoulantsFoulants
Marked IncreaseMarked Increase
(( >> 2x)2x)
Marked IncreaseMarked Increase
(( >> 2x)2x)
Marked DecreaseMarked Decrease
(( >> 50%)50%)
PluggagePluggage
MacroMacro
IncreaseIncrease Rapid MarkedRapid Marked
IncreaseIncrease
Rapid MarkedRapid Marked
DecreaseDecrease
Frequent Causes of Change
Change in Permeate TDS
Higher
“O” Ring Leakage
Membrane Damage
Higher Feed TDS
Low Product Flow
Low Brine Flow
Fouling
Scaling
Lower
Lower Feedwater
TDS
Initial
BioFouling
Frequent Causes of Change
Change in Pressure Drop
Higher
Biofouling
Scaling
Inorganic Fouling
Higher Flow Rates
Lower Feed Temp.
Lower
Lower Flow Rates
Higher Feed Temp.
Frequent Causes of Change
Change in Feed Pressure
Higher
Scaling
Pluggage
Higher Feed TDS
Lower Feed Temp.
Improper Valving
Lower
Higher Feed Temp.
Lower Feed TDS
Membrane Damage
Frequent Causes of Change
Change in Feed Chemistry
Chemistry Change Effect on System
pH Too High Membrane Damage
pH Too Low Membrane Damage
Cl2 outside Specs. Membrane Damage
Scaling Ions above Specs. Scaling
Increased SDI / Turbidity Fouling
Reverse Osmosis
Cleaning
When do I clean?
• When any ONE of the following changes:
 NPF by 10% - 15%
 Differential Pressure by 10% - 15%
 Salt Rejection by 10% - 15%
• Start planning your strategy at the first
indication of a minimum change!
Proper Cleaning Maintenance
NormalizedNormalized
PermeatePermeate
FlowrateFlowrate
TimeTime
Cleaning after 10Cleaning after 10--15% decline15% decline
NormalizedNormalized
PermeatePermeate
FlowrateFlowrate
TimeTime
Improper Cleaning MaintenanceImproper Cleaning Maintenance
Cleaning after >15% declineCleaning after >15% declineCleaning after >15% declineCleaning after >15% decline
Waiting tooWaiting too
longlong
to cleanto clean
reducesreduces
RORO
performanceperformance
Cleaning after aCleaning after a
1010--15% decline15% decline
maximizes ROmaximizes RO
performanceperformance
Cleaning Skid
5m5m
CFCF
DP
SS/PlasticSS/Plastic
CleaningCleaning
PumpPump
StrainerStrainer
CleaningCleaning
SolutionSolution
ReturnReturnPermeate ReturnPermeate Return
PermeatePermeate
SupplySupply
T
Isolate StagesIsolate Stages
P
P
F
Sample
TC
HeaterHeater
L
RecirculationRecirculation
DrainDrain
5m5m
CFCF
DP
SS/PlasticSS/Plastic
CleaningCleaning
PumpPump
StrainerStrainer
CleaningCleaning
SolutionSolution
ReturnReturnPermeate ReturnPermeate Return
PermeatePermeate
SupplySupply
T
Isolate StagesIsolate Stages
P
P
F
Sample
TC
HeaterHeater
L
TCTC
HeaterHeater
L
RecirculationRecirculation
DrainDrain
Cleaning
• Do Not Exceed Mftr. Specs!
– pH
– Pressure Drop
– Temperature
– Flow Rate
Cleaning
• Cleaning CF size < Operating CF size
• Use permeate as Make-up
• Mix Chemical according to instructions
• Utilize “maximum” conditions
• Dump “first system volume” (i.e., flush)
Cleaning
• Return permeate & concentrate to tank
• Make as little permeate as possible
(Open concentrate valve wide open)
• Pump Size is critical
How To Choose a Chemical Cleaner
• Cleaner Selected for:
– Membrane Type
– Characteristics of Foulant
– Convenience
• Optimum Service
• Acid Cleaners First
• Followed by Caustic Cleaners
Cleaning Solutions
Things to Remember
• Start planning to clean when:
– Differential Pressure changes 10%
– NPF changes 10%
– Salt Rejection changes 10%
Things to Remember
• Order of cleaning chemicals:
– Caustic/Acid (can vary with contamination)
– Acid/Caustic (can vary with contamination)
– Sanitization
• Waiting too long will cause irreversible
damage!
Keep Good Records
Membrane Cleaning Frequency
Cleaning Frequency
Quarterly or less
Every 1-3 months
Every month or more
Adequacy Estimate
Adequate
Marginal
Not adequate
Clean Until
• pH Doesn’t Change
• Color Doesn’t Change
• Flow Doesn’t Change
• Pressure Doesn’t Change
RO Element Test & Cleaning Stand
Feed
Pressure
Gauge
Permeate
Flowrate
Globe
Valve
Reject
Flowrate
Needle
Valve
Reject
Pressure
Gauge
Permeate
% Salt Rejection
Monitor
Differential
Pressure
Benefits of Maintaining an RO
• Reduced operating costs
• Reduced maintenance costs
• Reduced downtime
• Extended membrane life
• Improved water quality and output
Typical Treatment Scheme
MULTIMEDIA
FILTER
CHLORINE
COAGULANT
(CARBON FILTER
GREENSAND FILTER)
SODIUM
SOFTENER
ANTISCALANT
BISULFITE
ACID
CAUSTIC
TO WASTE
TREATMENT OR
COOLING TOWER
REVERSE
OSMOSIS TO ION
EXCHANGE
OR BFWFEED
WATER
Pretreatment Selection
Technique Controls
Multimedia Filters Suspended solids
Carbon Filters Suspended solids, organics, chlorine
Greensand Filters Suspended solids, iron, manganese
Sodium Softeners Hardness, scale formers, iron,
manganese, some suspended solids
Chlorine Microbes, organics
Bisulfite Free chlorine
Acid / Caustic Scale formers (acid), pH
Antiscalant Scale formers, foulants
Ultrafiltration Color or Bacteria
Recovery Scale
REVERSE OSMOSIS SUMMARY
• Understanding RO terms is important for successful
unit operation.
• Initial design is critical and will determine long term
permeate quality.
• Data collection and normalization is vital to
maintenance and trouble shooting. (RO Eye)
• Pretreatment key to keeping membranes
performing well. (Permacare, RO Trasar, Permafloc
and/or Ultrasoft, Ultrasand)
• Cleaning based on trends in normalized data.
(Permaclean)
Reverse osmosis module

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Reverse osmosis module

  • 2. Dam Pumping Raw Water Treatment Plant Pumping Wastewater Treatment Plant Collection Network Rain Agricultural Use IncinerationSludge Treatment Plant Collection Water Cycle Distribution Network Boiler Cooling Tower Process Discharge Water Cycle
  • 3. • Dramatic decrease in RO membrane prices (50% - 8yrs). • Increasing costs of chemicals (esp. NaOH) for IX systems. • Increased return on investment for reverse osmosis as pretreatment to an ion-exchange system. • Increased manufacturer awareness in properly designing pretreatment systems. • Increase in comfort level for operation of customer-owned RO systems. • Consistent water quality REASONS FOR INCREASED POPULARITY WITH REVERSE OSMOSIS
  • 4. RO Seminar Objectives – Reverse Osmosis Principles and Operation (Reverse Osmotic Pressure) – Designs and terminology – Operating parameters, problems, troubleshooting – Cleaning – Products and Equipment – Miscellaneous subjects
  • 9. Reverse Osmosis Applied Pressure, PF > Permeate Pressure, PP H2O H2O H2O Strong Solution Pure Water Flow Pure Water Osmotic Pressure, PO,F Osmotic Pressure, PO,P
  • 10. Types of Filtration TYPICAL FILTRATION CROSS-FLOW FILTRATION Solids on surface quickly foul the membrane Solids are swept away by continuous flow Feedwater FlowFeedwater Flow Purified waterPurified water
  • 11. CROSS-FLOW FILTRATION CROSS-FLOW FILTRATION •ONE INFLUENT •TWO EFFLUENT STREAMS •HIGH VELOCITY MINIMIZES MEMBRANE SCALING AND FOULING
  • 12. RO Skids typically have three major components. TO WASTE PRODUCTFEED CARTRIDGE FILTER HIGH-PRESSURE FEED PUMP PRESSURE VESSELS REVERSE OSMOSIS
  • 13. Cross Flow Filtration Methods Microfiltration Ultrafiltration Nanofiltration Reverse Osmosis Range Macro molecular Molecular Sub molecular Ionic Particle size 1.0 - 0.1 Micron 0.1 - 0.01 Micron 0.01 - 0.001 Micron <0.001 Micron Removes Suspended solids, Large colloids, Bacteria Proteins, Colloids, Organics Pyrogens, Divalent ions Virus Small Organics, Metals, Salts Molecular Weight >100,000 10,000 - 100,000 200 - 20,000 <300 Operating Pressure 10 psig (0.7 kg/cm2) 10 - 100 psig (0.7 kg-7.0/cm2) 150 -250 psig (14-17.5 kg/cm2) 150 - 800 psig (14- 56 kg/cm2) Pretreatment Needs Low Medium High High Capital Cost Low Medium High High
  • 15. Thin Film Composite Polyamide Membrane 0.2 micron 40 micron 120 micron Reinforcing Fabric Microporous Polysulfone Polyamide Ultrathin Barrier Layer
  • 17. Membrane Comparison Characteristic TFCCA Operating pH 2 - 11 Salt Rejection >99% Flux Rate (GPD/Ft2) 15-20 Bacteria Resistance Excellent Cl2 Tolerance 0.0 Physical Stability Better Max T (0F) 113 Feed Pressure 5 - 6.5 90-96% 12-16 Poor 0.2-1.0 Good 104 > 400 PSI < 200 PSI
  • 18. Membrane Comparison Cont. CA TFC Silica Rejection 85% 98% Nitrate Rejection 85% 94% Maximum SDI 5 5 3rd Year Compaction 20% 0% Hydrolysis 2 X None Characteristic
  • 19. Typical Passage of Ions IonIon %% SaltSalt PassagePassage % Salt Rejection% Salt Rejection AmmoniumAmmonium 55 9595 SodiumSodium 22 9898 PotassiumPotassium 22 9898 MagnesiumMagnesium <1<1 99+99+ StrontiumStrontium <1<1 99+99+ CalciumCalcium <1<1 99+99+ NitrateNitrate 1515 8585 BisilicateBisilicate 1010 9090 ChlorideChloride 22 9898 FluorideFluoride 22 9898 BicarbonateBicarbonate 22 9898 SulfateSulfate 11 9999 PhosphatePhosphate 11 9999 * TFC element rated for a 98%* TFC element rated for a 98% NaClNaCl rejectionrejection
  • 20. Membrane Configurations • Spiral Wound • Hollow Fiber • Tubular
  • 22. Flow Pattern for a Spiral Wound Element Spiral Wound Membrane Elements Wound Elements
  • 24. Hollow Fiber Membrane Element Feedwater P e r m e a t e Concentrate Concentrate Note: Only 4 hollow fibers are shown
  • 27. Glossary of Terms • Concentrate – Reject – Brine • Permeate – Product
  • 28. Reverse Osmosis Basics FEEDWATER 100 gpm 600 ppm TDS PERMEATE 75 gpm 30 ppm TDS 5% Salt Passage 75% Recovery CONCENTRATE 95% Salt Rejection 25 gpm 2310 ppm TDS 25% Concentrate
  • 29. What is RO Permeate and % Recovery? • Permeate is water recovered as product. • % Recovery = Permeate Flow Rate x100 – % Recovery calculates percent of feedwater that becomes product. – % Recovery describes performance of the system – Greater recovery=less waste=cost savings. – Recovery typically ranges from 50% to 75% (can go as high as 85%) – % Recovery and permeate quality are inversely related. REVERSE OSMOSIS Make-up Flow Rate
  • 31. What is RO Concentrate and % Rejection? • Concentrate (or Brine) is the waste from the RO. • Reject is a calculation of the percentage of solids/solutes in feedwater rejected by the membrane. – Typically ranges from 95% to 99+% for most ionic solutes and set by membrane manufacturer. – Greater % reject means better permeate quality. – Species dependant • Multi-valent ions (Ca2+, Mg2+) higher rejection • Monovalent ions (Na+, Cl-) lower rejection • Gases (O2, CO2) no rejection REVERSE OSMOSIS
  • 32. RO Systems – Reject Staging • Multi-stages for reject • Increased utilization of water – Incremental increase in investment – Minimal decrease in water quality – Multi - Pass • Product staging • Improves water quality – May eliminate the need for downstream polishing
  • 33. Two-Stage RO System - Reject Staging FEEDFEED PERMEATEPERMEATE HIGHHIGH PRESSUREPRESSURE PUMP TRAIN #1TRAIN #1 TRAIN #2TRAIN #2 ELEMENTSELEMENTS VESSELVESSEL 2:1 ARRAY2:1 ARRAY FEEDFEED REJECTREJECT CONCENTRATECONCENTRATE PERMEATEPERMEATE 1st STAGE1st STAGE 2nd STAGE2nd STAGE CONCENTRATECONCENTRATE
  • 34. Reject Staging • Increased Utilization of Water – Incremental Increase in Investment – Minimal Degradation in Water Quality
  • 35. Double Pass RO System 2nd Pass Concentrate Recycled * pH 9.0* pH 9.0 w/w/ NaOHNaOH PermeatePermeate FeedFeed 1st Pass Permeate 11 stst Pass Concentrate to Drain
  • 36. Double Pass • Applications: – Seawater (High TDS) – Ultra-high purity applications • Benefits of interstage pH adjustment – Improved Alkalinity Rejection – Improved Silica Rejection – Improved TOC Rejection
  • 38. What Are the Advantages of RO ? • Removes nonionic impurities and dissolved solids (i.e. organics, silica, bacteria) • Reduction of hazardous chemical storage and handling associated with ion exchange • Economic advantages increase with increasing feed TDS
  • 39. What Are the Disadvantages of RO? • Concentrate is rejected and this can be a significant volume of water. • RO membranes reject a fixed percentage of feedwater ions – Further treatment is required for many applications. • Ultimate filter which is easily fouled: – Increasing operating costs – Reducing membrane life
  • 40. Typical Operating Cost Breakdown Membrane Replacement 12% Chemicals 14% Labor 25% Other 5% Electrical 44%
  • 42. Membrane Problems  Scaling - Mineral Salts - Silica  Fouling - Metal Oxides - Colloidal Silt & Crud - Biological & Organics  Hydrolysis & Chemical Attack - pH, Temperature, Oxidants, Biodegradation  Compaction
  • 43. REVERSE OSMOSIS •80% to 90% of problems are related to pretreatment of RO Feedwater •The purpose of pretreatment is to prevent • Membrane Fouling • Membrane Scaling • Membrane Degradation
  • 44. REVERSE OSMOSIS Effects of Fouling, Scale, Degradation Poor Permeate Quality Frequent cleaning Increased Operating Pressure Increased O&M cost Membrane Replacement
  • 45. RO Fouling CategoryCategory ExamplesExamples SourcesSources Scaling SaltsScaling Salts CaCOCaCO33 FeedwaterFeedwater CaSOCaSO44 Sulfuric AcidSulfuric Acid BaBa // SrSr -- SOSO44 CaFCaF22 SiOSiO22 -- ComplexesComplexes Metal OxidesMetal Oxides IronIron FeedwaterFeedwater ManganeseManganese CorrosionCorrosion AluminumAluminum ClarifiersClarifiers ColloidsColloids SiltSilt Surface WatersSurface Waters RustRust Corroding PipesCorroding Pipes BiologicalBiological Organic SlimesOrganic Slimes NonNon--ClCl22 FeedFeed BacteriaBacteria OffOff--line Systemsline Systems OrganicOrganic PolymerPolymer Coagulant OverfeedCoagulant Overfeed HydrocarbonHydrocarbon Process LeaksProcess Leaks
  • 46. Scale • Cause: – Salt exceeds solubility limits due to concentration effects • Prevention: – Reduce Recovery – Acid Feed (CaCO3) – Sodium Zeolite Softening – Antiscalant
  • 50. Metal Oxide Iron, Manganese and Aluminum • Cause: – Feedwater – Corrosion in system piping – Clarifier carryover • Prevention: – Oxidation & Filtration – Greensand Filtration (Mn) – Softening (Fe & Mn) – Chemical Antifoulant
  • 52. REVERSE OSMOSIS •RO For: • DOSAGE CONTROL • LEAK ANALYSIS DIAGNOSTICS • TRUE SYSTEM RECOVERY • MEMBRANE INTEGRITY • COST CONTROL SCALE CONTROL
  • 53. Components of RO TRASAR® Trasar 8000 Handheld Fluorometer for Monitoring and Diagnostics Trasar 3000 Fluorometer for On-line Monitor & Control
  • 54. 120 MW CCGT Cogeneration Plant, Florida • Description of demineralization system – Water source: city water – Pre-treatment: feed water dechlorination – Reverse osmosis: 2X100 gpm systems – Post-treatment: mixed-bed ion exchange column • Performance issues – Fouling of membrane elements resulting in frequent cleanings – Poor permeate quality resulting in frequent regeneration of polishing ion exchange bed.
  • 55. Active control of scale inhibitor dosage 0 5 10 15 20 25 30 0 50 100 150 200 250 Hours of Continuous Operation PPMasAntiscalant Before Control After Control Reduced membrane fouling. 0 5 10 15 20 25 30 0 20 40 60 80 100 120 140 160 180 200 Hours of Continuous Operation ppmantiscalant Actual Dose Target Dose & Control Limits
  • 56. RO TRASAR® Benefits: 120 MW CCGT Cogeneration Plant > $37,600/yrTotal Savings TBD88%Every 800K galEvery 100K galPolishing IX regeneration $6,00050%4 yrs life2 yr lifeMembrane replacement $26,00085%4 per year26 per yearCleaning $5,60025%9 ppm12 ppmAntiscalant $/yr%AfterBefore Savings
  • 57. Colloids • Cause: – Surface water – Corrosion in system piping - (Line all vessels) • Prevention: – Coagulation & filtration – Zeolite softening – Chemical Antifoulant
  • 58. Bacteria, Slime • Cause: – Surface water – Non-Cl2 Feed – Off-Line RO System • Prevention: – Biocide • Cl2 residual – Dechlorination • Non-Oxidizing Biocide • UV Sterilization
  • 60. Organic • Cause: – Polymer overfeed – Surface Water – Process Leaks • Prevention for Polymer Overfeed: – Streaming Current Detector – Sodium Zeolite Softener – Inorganic Coagulant
  • 61. Hydrolysis & Chemical Attack CA MEMBRANES • Microbio growth present • pH < 5.0 or > 6.5 • Temperatures > 104 oF (40 0C) • Exposed to direct sunlight TFC MEMBRANES • Oxidants in feedwater (i.e. Cl2, O3) • Temperatures > 112 oF (44 0C) • Exposed to direct sunlight
  • 63. Results of Membrane Problems • Reduced water quality – Shorter run lengths on downstream IX • Premature membrane replacement • Higher operating costs
  • 65. Monitoring • Pretreatment – 90% of operational problems are found here • System – 10% of operational problems are found here
  • 66. RO System Monitoring • Pretreatment monitoring - Silt Density (SDI), Turbidity, pH, Oxidants Particle Size and Counts - Temperature, Pressure, TDS - Foulants (bacteria, metals, hardness, silica)
  • 67. RO System Monitoring • Performance monitoring - Percent salt rejection - Normalized permeate flowrate - Differential pressure
  • 68. Pretreatment • Silt Density Index (SDI) • Langlier Saturation Index (LSI) • Stiff Davis Index (TDS >4,000 mg/L) • Feedwater Analysis
  • 69. Silt Density Index (SDI) • Empirical indication of potential fouling • Based on rate of plugging a 0.45m filter • Hollow Fiber SDI < 3.0 • Spiral Wound SDI < 5.0 • Typical Well Water SDI < 3 • Typical Surface Water SDI > 6
  • 70. Silt Density Index SDI = PSDI = P3030 // T = (1T = (1 -- ttii // ttff) * 100) * 100 TT SDI = PSDI = P3030 // T = (1T = (1 -- ttii // ttff) * 100) * 100 TT FeedFeed SupplySupply (30(30--8080 psig)psig) PressurePressure RegulatorRegulator PressurePressure GaugeGauge ByBy--Pass toPass to draindrain FilterFilter HolderHolder FilterFilter HolderHolder
  • 71. Langlier Saturation Index (LSI) • Indicates the potential for CaCO3 scale • LSI > 0 “indicates scaling” • Calculation: – Computer programs – Permutit Handbook
  • 73. Feedwater Analysis • Minimal water test includes – Ca, Mg, Fe, Al, Silica – SO4, Alkalinity, pH, Conductivity – SDI – TOC – Color • Full water analysis should include analysis scaling/fouling contaminants
  • 74. Additional Pretreatment • Turbidity • pH • Oxidants • Temperature • Pressure • TDS / Conductivity • Foulants - bacteria, metals, hardness, silica etc.
  • 75. Affect of SDI on Flux & % Recovery per Element Feed source SDI Max. Flux (gal/ft2/day) Max. % Recovery RO permeate <1 25 30% Well water <3 20 19% Surface supply <3 17 17% Surface/softened <5 16 15% Seawater <5 10 13% Guidelines for 8 inch Filmtec element
  • 76. Affect of SDI on Flux by System Feed source SDI Max. Flux (gal/ft2/day) RO permeate <1 21 – 25 Well water <3 16 – 20 Surface supply <3 13 – 17 Surface supply <5 10 – 16 Nalco recommendations for longer membrane life Nalco Recommendation 22 16 14 13
  • 77. Effect of Temperature on Permeate Flowrate TEMPERATURETEMPERATURE --1.11.1 4.44.4 10.010.0 15.615.6 21.121.1 26.726.7 32.232.2 37.837.8 43.343.3 PermeateFlowrate,PermeateFlowrate, %ofDesign%ofDesign 7070 8080 9090 100100 110110 6060 4040 5050 6060 7070 8080 9090 120120 1001003030 110110 00 FF 00 CC
  • 78. System Monitoring The Critical 3 • Percent Salt Rejection • Normalized Permeate Flowrate (NPF) • Differential Pressure (ΔP) (Use Computer and Trend Data)
  • 79. Salt Rejection % Rejection = (TDSfeed - TDSPermeate) x 100 TDSfeed Common to use conductivity measurement as an indication of TDS
  • 80. Net Differential Pressure DP = Pf - Pc Pf = feed pressure Pc = concentrate pressure DP differential pressure, “delta P” or pressure drop
  • 81. Normalized Permeate Flowrate Flownormalize : Qn = NDP(start-up) * FT * Qp NDP(daily) Pf = Feed Pressure Pp = Permeate Pressure PO,F = Osmotic Press. Feed PO,C = Osmotic Press. Brine FT = Temp. Correction Factor Qp = Permeate Flowrate NDP = Pf - Pp - PO NDP = Pf - Pp - PO
  • 82. Net Driving Pressure Available Pressure to “Drive” the Process • NDP = PF + PO,P - PP - PO,F • Brackish water PO,P = 0 • Average NDP • NDP = PF - PP - PO,F • NDP = (PF+Pc) - (PP+PP) - (PO,F+PO,C) 2 2 2
  • 83. Trending & Normalization • Permeate Flow • Differential Pressure • Salt Rejection Enter Data Using Nalco “RO Trend”
  • 84. Effect of Driving Pressure on Permeate FlowratePermeateFlowrate,%PermeateFlowrate,% PercentRejection,%PercentRejection,% 20%20% 40%40% 60%60% 80%80% 100%100% 0%0% 20%20% 40%40% 60%60% 80%80% 100%100% 120%120% 20%20% 40%40% 60%60% 80%80% 100%100% 0%0% DRIVING PRESSUREDRIVING PRESSURE
  • 86. Raw Data Vs. Normalized Data
  • 87. Start Up Information • Collect Initial Data within first 24 to 72 hours • Everything is compared to “Start up” data
  • 88. Daily Operation & Performance Parameters Date Operator’s initials Feedwater silt density index (SDI) Feedwater turbidity Feedwater temperature Feedwater temperature correction factor Feedwater pH Oxidant concentration (i.e. Cl, sanitizer) Feedwater conductivity or TDS Permeate conductivity or TDS Reject conductivity or TDS Percent salt rejection (calculated) Feed (membrane) pressure Permeate pressure Reject pressure Net differential pressure (calculated) Net driving pressure Feedwater flowrate Permeate flowrate Reject flowrate Normalized permeate flowrate (calculated) Percent recovery (calculated) Use Computers to Trend this Data
  • 89. Trending Data Using the Performance Variable Feed Flow Rate (gpm) 120 110 100 90 100 90 80 100 90 80 40 30 20 Differential Pressure Feed Flow Rate Start-up Membrane Elements cleaned Leaking O-ring Replaced Net Differential Pressure (psig) % Reject Normalized Permeate Flow Rate (gpm)
  • 90. REVERSE OSMOSIS •RO-EYE • REVERSE OSMOSIS MONTIROING AND CONTROL SYSTEM • Real time data monitoring • Data normalization • TRASAR control T M
  • 92. Product ConcentrateFeed Brine becomes more concentrated Feed Flowrate Decreases Flow Through a Pressure Vessel
  • 93. Indications of Trouble Change • Salt Rejection • Differential Pressure • Normalized Permeate Flow • Others
  • 94. Trouble Shooting Changes • Check Instrument Calibrations – Compare Percent Recovery by Conductivity Vs. Flow • Identify the Location of the Decline – Front end Vs. Back end, Stage 1 Vs. Stage 2 • Investigate Potential Causes of the Problem – Use both visual and analytical data • Correct the Potential Cause of the Problem
  • 95. Troubleshooting Instrument Calibration • Compare Recovery Calculations – Conductivity Vs. Flow • Pressure Meter Change Out – Quick Disconnects • Hand Held Vs. On-line Instrumentation • Thermometers
  • 96. Trouble Shooting / Changes in Salt Rejection • Check Individual Pressure Vessel Performance • Probe the Pressure Vessel (Spiral Wound) • Individual Membrane Testing – Single Element Test Skid Identify the Location of the Decline
  • 97. Check Individual Pressure Vessel Performance First Stage Pressure Vessel Profile: Pressure Vessel # Permeate TDS (ppm) 1 25 2 22 3 49 4 20 Second Stage Pressure Vessel Profile: 5 36 6 34 Example - 4:2 Array
  • 98. When to Probe • High salt passage • Individual pressure vessels have high conductivity
  • 99. Individual Element Performance • Probe the Pressure Vessel (Spiral Wound) – 1/4” Tubing into Permeate Line – Conductivity versus Penetration • Location of Problem – Check front / mid / end each element – Note direction of feed water flow
  • 100. 1/4” Polypropylene Tubing RO Vessel Containing 6 Elements Probing a Pressure Vessel Probe every 8 inches to determine membrane or o-ring damage
  • 101. Membrane Element # Permeate TDS (ppm) 1 Lead End 25 2 23 3 25 4 21 5 Tail End 54 Probing a Pressure Vessel Remember to Note Feedwater Direction
  • 102. Troubleshooting Individual Membrane Elements • Individual Membrane Testing – In House • Non-destructive – Single Element Test Stand – Autopsy • Potentially Destructive • More detailed Information`
  • 103. Problems CauseCause General SymptomsGeneral Symptoms Salt PassageSalt Passage PermeatorPermeator DD PP Product FlowProduct Flow ScalantsScalants Carbonates, Sulfates,Carbonates, Sulfates, PhosphatesPhosphates SignificantSignificant Increase (10Increase (10--25%)25%) Slight to ModerateSlight to Moderate IncreaseIncrease (10(10 -- 50%)50%) Slight DecreaseSlight Decrease (( << 10%)10%) Metal OxidesMetal Oxides FoulantsFoulants Iron, Manganese etc.Iron, Manganese etc. Rapid MarkedRapid Marked Increase (Increase ( >> 2x)2x) Rapid MarkedRapid Marked Increase (Increase ( >> 2x)2x) Rapid MarkedRapid Marked Decrease (Decrease ( >> 50%)50%) ColloidalColloidal GradualGradual GradualGradual GradualGradual FoulantsFoulants mostly Aluminum Silicatesmostly Aluminum Silicates Marked IncreaseMarked Increase (( >> 2x)2x) Marked IncreaseMarked Increase (( >> 2x)2x) Marked DecreaseMarked Decrease (( >> 50%)50%) BiofilmBiofilm FoulantsFoulants Marked IncreaseMarked Increase (( >> 2x)2x) Marked IncreaseMarked Increase (( >> 2x)2x) Marked DecreaseMarked Decrease (( >> 50%)50%) PluggagePluggage MacroMacro IncreaseIncrease Rapid MarkedRapid Marked IncreaseIncrease Rapid MarkedRapid Marked DecreaseDecrease
  • 104. Frequent Causes of Change Change in Permeate TDS Higher “O” Ring Leakage Membrane Damage Higher Feed TDS Low Product Flow Low Brine Flow Fouling Scaling Lower Lower Feedwater TDS Initial BioFouling
  • 105. Frequent Causes of Change Change in Pressure Drop Higher Biofouling Scaling Inorganic Fouling Higher Flow Rates Lower Feed Temp. Lower Lower Flow Rates Higher Feed Temp.
  • 106. Frequent Causes of Change Change in Feed Pressure Higher Scaling Pluggage Higher Feed TDS Lower Feed Temp. Improper Valving Lower Higher Feed Temp. Lower Feed TDS Membrane Damage
  • 107.
  • 108.
  • 109.
  • 110.
  • 111. Frequent Causes of Change Change in Feed Chemistry Chemistry Change Effect on System pH Too High Membrane Damage pH Too Low Membrane Damage Cl2 outside Specs. Membrane Damage Scaling Ions above Specs. Scaling Increased SDI / Turbidity Fouling
  • 113. When do I clean? • When any ONE of the following changes:  NPF by 10% - 15%  Differential Pressure by 10% - 15%  Salt Rejection by 10% - 15% • Start planning your strategy at the first indication of a minimum change!
  • 114. Proper Cleaning Maintenance NormalizedNormalized PermeatePermeate FlowrateFlowrate TimeTime Cleaning after 10Cleaning after 10--15% decline15% decline NormalizedNormalized PermeatePermeate FlowrateFlowrate TimeTime Improper Cleaning MaintenanceImproper Cleaning Maintenance Cleaning after >15% declineCleaning after >15% declineCleaning after >15% declineCleaning after >15% decline Waiting tooWaiting too longlong to cleanto clean reducesreduces RORO performanceperformance Cleaning after aCleaning after a 1010--15% decline15% decline maximizes ROmaximizes RO performanceperformance
  • 115. Cleaning Skid 5m5m CFCF DP SS/PlasticSS/Plastic CleaningCleaning PumpPump StrainerStrainer CleaningCleaning SolutionSolution ReturnReturnPermeate ReturnPermeate Return PermeatePermeate SupplySupply T Isolate StagesIsolate Stages P P F Sample TC HeaterHeater L RecirculationRecirculation DrainDrain 5m5m CFCF DP SS/PlasticSS/Plastic CleaningCleaning PumpPump StrainerStrainer CleaningCleaning SolutionSolution ReturnReturnPermeate ReturnPermeate Return PermeatePermeate SupplySupply T Isolate StagesIsolate Stages P P F Sample TC HeaterHeater L TCTC HeaterHeater L RecirculationRecirculation DrainDrain
  • 116. Cleaning • Do Not Exceed Mftr. Specs! – pH – Pressure Drop – Temperature – Flow Rate
  • 117. Cleaning • Cleaning CF size < Operating CF size • Use permeate as Make-up • Mix Chemical according to instructions • Utilize “maximum” conditions • Dump “first system volume” (i.e., flush)
  • 118. Cleaning • Return permeate & concentrate to tank • Make as little permeate as possible (Open concentrate valve wide open) • Pump Size is critical
  • 119. How To Choose a Chemical Cleaner • Cleaner Selected for: – Membrane Type – Characteristics of Foulant – Convenience • Optimum Service • Acid Cleaners First • Followed by Caustic Cleaners
  • 121. Things to Remember • Start planning to clean when: – Differential Pressure changes 10% – NPF changes 10% – Salt Rejection changes 10%
  • 122. Things to Remember • Order of cleaning chemicals: – Caustic/Acid (can vary with contamination) – Acid/Caustic (can vary with contamination) – Sanitization • Waiting too long will cause irreversible damage!
  • 124. Membrane Cleaning Frequency Cleaning Frequency Quarterly or less Every 1-3 months Every month or more Adequacy Estimate Adequate Marginal Not adequate
  • 125. Clean Until • pH Doesn’t Change • Color Doesn’t Change • Flow Doesn’t Change • Pressure Doesn’t Change
  • 126. RO Element Test & Cleaning Stand Feed Pressure Gauge Permeate Flowrate Globe Valve Reject Flowrate Needle Valve Reject Pressure Gauge Permeate % Salt Rejection Monitor Differential Pressure
  • 127. Benefits of Maintaining an RO • Reduced operating costs • Reduced maintenance costs • Reduced downtime • Extended membrane life • Improved water quality and output
  • 128. Typical Treatment Scheme MULTIMEDIA FILTER CHLORINE COAGULANT (CARBON FILTER GREENSAND FILTER) SODIUM SOFTENER ANTISCALANT BISULFITE ACID CAUSTIC TO WASTE TREATMENT OR COOLING TOWER REVERSE OSMOSIS TO ION EXCHANGE OR BFWFEED WATER
  • 129. Pretreatment Selection Technique Controls Multimedia Filters Suspended solids Carbon Filters Suspended solids, organics, chlorine Greensand Filters Suspended solids, iron, manganese Sodium Softeners Hardness, scale formers, iron, manganese, some suspended solids Chlorine Microbes, organics Bisulfite Free chlorine Acid / Caustic Scale formers (acid), pH Antiscalant Scale formers, foulants Ultrafiltration Color or Bacteria Recovery Scale
  • 130. REVERSE OSMOSIS SUMMARY • Understanding RO terms is important for successful unit operation. • Initial design is critical and will determine long term permeate quality. • Data collection and normalization is vital to maintenance and trouble shooting. (RO Eye) • Pretreatment key to keeping membranes performing well. (Permacare, RO Trasar, Permafloc and/or Ultrasoft, Ultrasand) • Cleaning based on trends in normalized data. (Permaclean)