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By Peter Fox and Mara Ramos
Presented to the AZ Water Quality Association,
November 19th, 2010, Tempe, AZ
Evaluation of Alternatives to Ion
Exchange
Many potential factors to consider
Scaling of Hot Water Heater
Scaling/streaking of sinks, toilets, dishes, etc.
Taste
Water Use
Energy Use – both treatment device and hot water
heater
This study will focus primarily on scaling since this can be
scientifically quantified.
Related Factors not Considered in
this Study
Domestic Water Heating uses more energy than urban
water/wastewater treatment and distribution.
In 2008, CDC acknowledged more waterborne disease
from premise plumbing than from traditional
pathogens (Legionella, mycobacterium).
Recent research shows autotrophic growing on
sacrificial anodes add AOC in hot water heaters.
Scale certainly affects these factors.
Quantifying Scale Formation
DVGW – German Association of Gas and Water
Boards is responsible for certifying technologies for
safety, hygiene and performance capabilities.
DVGW – W512 is the test used to determine
effectiveness of water conditioning devices installed to
prevent or reduce scaling in drinking water heating
systems and secondary installations.
The W512 testing protocol is what we are basing our
experimental methodology on.
Operate a system for twenty days and quantify scale
formed in a water heater – more later.
Scale Prevention Technologies
Chemical Treatment – Chemical Softening, Ion
Exchange, Scale Inhibitors
Physical Water Treatment (PWT) – Commonly used to
describe the devices we will consider as alternatives to
ion exchange. No chemicals added.
PWT devices may be classified as scale inducing or
scale preventing.
Scale Inducing Technologies
These technologies work by inducing scale to form
before a hot water heater thereby reducing the scale
forming potential of the water.
Template Assisted Crystallization – Catalyzes the
formation of sub micron crystals that remain in the
water as colloidal matter
Electrically Induced Precipitation – An applied current
induces the formation of “soft” scale on an electrode
that must be periodically cleaned
Scale Preventing Technologies
These technologies modify the water content to
prevent scale formation.
Capacitive Deionization – Reduces Concentrations of
all ions to reduce scale formation
Electromagnetic Devices (???) – Claim to cause
formation of soft precipitates that remain colloidal
(amorphous aragonite and vaterite instead of
crystalline calcite)
Other Static Devices – claim to cause effects similar to
electromagnetic devices
Template Assisted Crystallization
Technology Has Many Different
Applications – Relatively new to water
treatment
A Catalytic Reaction is carried out on a
template – usually a honeycomb
polystyrene structure
Can be used to make well ordered
micrometric and nanometric
structures
ZnO nanosheets, Photonic Balls
Template Assisted Crystallization
Uses Polymeric Beads with nucleation sites to convert
dissolved hardness into microscopic crystals
Once crystals grow to the template size, the crystals
are released and remain in the water without forming
scale
Calcite or Aragonite???
DVGW Certified
Operates as a fluidized bed to maximize surface area
and effectiveness
Commercially available for a variety of flowrates.
Electrically Induced Precipitation
Uses Direct Current to form Soft Precipitate
DVGW certified
Maximum Power required – 100W
Length of Operation may be limited since use of DC is
dangerous
Backwash Water is required to clean electrode –
Process Control not clear
Electrically Induced Precipitation -
Claims
CaCO3 crystals appear to be aragonite – needle like
crystals that do not form scale
Capacitive Deionization –
Apply DC current – 2 amps at 110 V
Ions move to anode and cathode and attach to
nanomaterials?
Once saturated, must regenerate and flush
Citric Acid cleaning may be necessary
Technology has been in development for 50 years
Capacitive Deionization
Commercially Available for
Whole House Treatment
80-95% Salt Removal
75% water recovery – is this
acceptable?
Semi-Automatic Citric Acid
Clean
Dial for Taste – where do we
set it?
Electromagnetic Technologies
Literature has mixed results – successful tests result in
aragonite or vaterite instead of calcite
In theory, a magnetic field should not affect water but
“structured” distilled water has been documented
Recent studies have shown that dissolved oxygen may
play a role – dioxygen is paramagnetic
Silica may also play a role in scale prevention according
to some studies
Carbonate might also be important
Electromagnetic Technologies
Basic Device is a wire wrapped
around a pipe that transmits
electronic frequencies (magnetic
field) to cause a physical change
Summary of Technologies
Template Assisted Crystallization – Scale Inducing
New to water industry and rapidly developing
technology
No Power or Backwash required
Life of Media – recommended change 12-18 months
Electrically Induced Precipitation – Scale Inducing
Relatively new to water industry
Power and periodic backwash required
Summary of Technologies
Capacitive Deionization – Technology in Development
for 5o years with limited application
Requires Power and 25% reject water
Periodic Citric Acid Clean
Can control removal of salt for taste
Electromagnetic Technologies – Been used for many
years with sporadic documentation
Power required
No backwash required
Filters sometimes sold with the technology
Testing Methodology
Protocol based on DVGW W512 test to assess control
of scale formation
Pump 130 L of water through an electronically heated
10-L reservoir for 20 days
After test is complete, determine the quantity of scale
formed on the heating element and the reservoir
The test has a specific calculation to determine if a
scale prevention device will be certified – this is based
on a specified water quality and is not applicable to our
testing where different waters will be tested
Testing Apparatus: Side view
Alternative Conditioning Devices
(Electrical Precipitation)
(Template Assisted
Crystallization)
(Electro Magnetic Water
Treatment)
This wire will be wrapped
around the PVC pipe as it is on
the copper pipe shown.
DVGW W512 Protocol Issues
Requires a temperature of 80oC. Domestic water
heaters operate between 40-60oC. It would be more
realistic to operate the tests at 60oC.
Requires an unrealistically low watt density. We used a
watt density typical of an electric water heater.
Assessment of Scale Formation
The quantity of calcium and magnesium in any scale
formed is quantified by dissolution in acid and
subsequent analysis
Scale on the Heating Coil and the Container Walls is
quantified in terms of the number of moles of Ca and
Mg ions
An effectiveness factor is calculate by comparing the
results with a treatment device with untreated water
Effectiveness Factor (EF)
EF = (Ca +Mg)M untreated – (Ca+Mg)M treated
(Ca +Mg)M untreated
The DVGW certifies a device with an EF greater than 0.8
For this study the EF will be used as a relative measure
without applying any pass fail criteria.
Waters to be Tested
City of Tempe Tap water – Salt River (180 mg/l of
hardness as CaCO3)
Colorado River Water – Central Arizona Project
treated at Scottsdale Water Campus (150-220 mg/L of
hardness as CaCO3)
Groundwater – South Scottsdale at Pima Park
Treatment Facility – Treated by Air Stripping (200-250
mg/L of hardness as CaCO3)
Santa Clara/San Jose Sub-basin Groundwater –
Completed in California
Schedule – Months of Testing at
ASU
Salt River Water – Three months
First Two Runs - No Treatment and Ion exchange
Next Four Runs - Four Alternative Treatment Devices
Colorado River water – Two months – Four Alternative
Treatment Devices
South Scottsdale Groundwater – Two months – Four
Alternative Treatment Devices
Salt River Water – Two Months – Repeat Tests at 60oC
RESULTS -Tempe Tap - Untreated
Tempe Tap – Template Assisted
Crystallization
Tempe Tap – Electromagnetic
Tempe Tap – Electrically Induced
Precipitation
Tempe Tap – Capacitive
Deionization
Almost all scale measured
was found in the bath.
Results Summary
Water Type
Treatment device
used
Scale
scraped off
of heating
element
(g)
% Ca as
CaCO3
in
scale
forme
d
Ca formed
in solid
scale
precipitate
(g Ca as
CaCO3)
Scale from
bath and
heating
element
dissolved
with HCl
(g Ca as
CaCO3)
Total
calcium
formed
during
test
(g Ca as
CaCO3)
Photo of
heating
element
with scale
Tempe tap
water
No Treatment - NA 0.0 8.4 8.4
Template Assisted
Crystallization
0.0 NA 0.0 0.3 0.3
Electrically Induced
Precipitation
0.7 87.2 0.6 3.5 4.1
Electromagnetic 1.4 87.2 1.3 3.6 4.9
Capacitive
Deionization
0.0 NA 0.0 1.4 1.4
Ion Exchange
Preliminary Results
Template Assisted Crystallization worked best
Capacitive Deionization worked well enough to pass
DVGW test
Both Electromagnetic treatment and electrically
induced precipitation reduced scale formation
significantly. The scale formed was “soft” scale that
easily brushed off. The test does not determine long
term accumulation
A rapid assessment test would be
highly desirable
Both Template Assisted Crystallization and
Electromagnetic Devices might create microscopic
forms of CaCO3 that remain suspended
Use this fact to develop a rapid assessment test
Two possible methods
Filtration to separate suspended CaCO3
Hach Kit – EDTA will only measure soluble Ca and Mg
Surface Tension, X-ray diffraction, spectroscopy, etc.
Results with Hach Kit using
Electromagnetic Treatment
Tempe Tap Water Total Hardness After Acidification
No Treatment 163.2
After Electromagnetic
Treatment
123.2 156.8
After Template Assisted
Crystallization Treatment
168 167
Langeleir Index with No Treatment = +0.24
Langeleir Index After EM Treatment = -0.08
IS THIS POSSIBLE?
X Ray Diffraction
0
500
1000
1500
2000
2500
3000
3500
4000
4500
5000
10 15 20 25 30 35 40 45 50 55 60
Intensity
Angle
XRD Magnetic Treatment
0
1000
2000
3000
4000
5000
6000
10 15 20 25 30 35 40 45 50 55 60
Intensity
Angle
XRD Untreated
Both have calcite patterned peaks.
RAMAN Spectroscopy
RAMAN Spectrum of water
Untreated
Magnetic Treatment
Acceptance??? – not up to Water
Reuse Foundation or Researchers
IAPMO is developing a standard protocol based on the
DVGW – National Sanitation Foundation can then
certify
Industrial/Commercial applications are strong
candidates – understand maintenance issues and
desire cost savings
Homeowners – depends on green movement and
willingness to accept potential problems (Dissolved
CO2, etc.)

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Presentation to AZ WQA (1) [Read-Only]

  • 1. By Peter Fox and Mara Ramos Presented to the AZ Water Quality Association, November 19th, 2010, Tempe, AZ
  • 2. Evaluation of Alternatives to Ion Exchange Many potential factors to consider Scaling of Hot Water Heater Scaling/streaking of sinks, toilets, dishes, etc. Taste Water Use Energy Use – both treatment device and hot water heater This study will focus primarily on scaling since this can be scientifically quantified.
  • 3. Related Factors not Considered in this Study Domestic Water Heating uses more energy than urban water/wastewater treatment and distribution. In 2008, CDC acknowledged more waterborne disease from premise plumbing than from traditional pathogens (Legionella, mycobacterium). Recent research shows autotrophic growing on sacrificial anodes add AOC in hot water heaters. Scale certainly affects these factors.
  • 4. Quantifying Scale Formation DVGW – German Association of Gas and Water Boards is responsible for certifying technologies for safety, hygiene and performance capabilities. DVGW – W512 is the test used to determine effectiveness of water conditioning devices installed to prevent or reduce scaling in drinking water heating systems and secondary installations. The W512 testing protocol is what we are basing our experimental methodology on. Operate a system for twenty days and quantify scale formed in a water heater – more later.
  • 5. Scale Prevention Technologies Chemical Treatment – Chemical Softening, Ion Exchange, Scale Inhibitors Physical Water Treatment (PWT) – Commonly used to describe the devices we will consider as alternatives to ion exchange. No chemicals added. PWT devices may be classified as scale inducing or scale preventing.
  • 6. Scale Inducing Technologies These technologies work by inducing scale to form before a hot water heater thereby reducing the scale forming potential of the water. Template Assisted Crystallization – Catalyzes the formation of sub micron crystals that remain in the water as colloidal matter Electrically Induced Precipitation – An applied current induces the formation of “soft” scale on an electrode that must be periodically cleaned
  • 7. Scale Preventing Technologies These technologies modify the water content to prevent scale formation. Capacitive Deionization – Reduces Concentrations of all ions to reduce scale formation Electromagnetic Devices (???) – Claim to cause formation of soft precipitates that remain colloidal (amorphous aragonite and vaterite instead of crystalline calcite) Other Static Devices – claim to cause effects similar to electromagnetic devices
  • 8. Template Assisted Crystallization Technology Has Many Different Applications – Relatively new to water treatment A Catalytic Reaction is carried out on a template – usually a honeycomb polystyrene structure Can be used to make well ordered micrometric and nanometric structures ZnO nanosheets, Photonic Balls
  • 9. Template Assisted Crystallization Uses Polymeric Beads with nucleation sites to convert dissolved hardness into microscopic crystals Once crystals grow to the template size, the crystals are released and remain in the water without forming scale Calcite or Aragonite??? DVGW Certified Operates as a fluidized bed to maximize surface area and effectiveness Commercially available for a variety of flowrates.
  • 10. Electrically Induced Precipitation Uses Direct Current to form Soft Precipitate DVGW certified Maximum Power required – 100W Length of Operation may be limited since use of DC is dangerous Backwash Water is required to clean electrode – Process Control not clear
  • 11. Electrically Induced Precipitation - Claims CaCO3 crystals appear to be aragonite – needle like crystals that do not form scale
  • 12. Capacitive Deionization – Apply DC current – 2 amps at 110 V Ions move to anode and cathode and attach to nanomaterials? Once saturated, must regenerate and flush Citric Acid cleaning may be necessary Technology has been in development for 50 years
  • 13. Capacitive Deionization Commercially Available for Whole House Treatment 80-95% Salt Removal 75% water recovery – is this acceptable? Semi-Automatic Citric Acid Clean Dial for Taste – where do we set it?
  • 14. Electromagnetic Technologies Literature has mixed results – successful tests result in aragonite or vaterite instead of calcite In theory, a magnetic field should not affect water but “structured” distilled water has been documented Recent studies have shown that dissolved oxygen may play a role – dioxygen is paramagnetic Silica may also play a role in scale prevention according to some studies Carbonate might also be important
  • 15. Electromagnetic Technologies Basic Device is a wire wrapped around a pipe that transmits electronic frequencies (magnetic field) to cause a physical change
  • 16. Summary of Technologies Template Assisted Crystallization – Scale Inducing New to water industry and rapidly developing technology No Power or Backwash required Life of Media – recommended change 12-18 months Electrically Induced Precipitation – Scale Inducing Relatively new to water industry Power and periodic backwash required
  • 17. Summary of Technologies Capacitive Deionization – Technology in Development for 5o years with limited application Requires Power and 25% reject water Periodic Citric Acid Clean Can control removal of salt for taste Electromagnetic Technologies – Been used for many years with sporadic documentation Power required No backwash required Filters sometimes sold with the technology
  • 18. Testing Methodology Protocol based on DVGW W512 test to assess control of scale formation Pump 130 L of water through an electronically heated 10-L reservoir for 20 days After test is complete, determine the quantity of scale formed on the heating element and the reservoir The test has a specific calculation to determine if a scale prevention device will be certified – this is based on a specified water quality and is not applicable to our testing where different waters will be tested
  • 20. Alternative Conditioning Devices (Electrical Precipitation) (Template Assisted Crystallization) (Electro Magnetic Water Treatment) This wire will be wrapped around the PVC pipe as it is on the copper pipe shown.
  • 21. DVGW W512 Protocol Issues Requires a temperature of 80oC. Domestic water heaters operate between 40-60oC. It would be more realistic to operate the tests at 60oC. Requires an unrealistically low watt density. We used a watt density typical of an electric water heater.
  • 22. Assessment of Scale Formation The quantity of calcium and magnesium in any scale formed is quantified by dissolution in acid and subsequent analysis Scale on the Heating Coil and the Container Walls is quantified in terms of the number of moles of Ca and Mg ions An effectiveness factor is calculate by comparing the results with a treatment device with untreated water
  • 23. Effectiveness Factor (EF) EF = (Ca +Mg)M untreated – (Ca+Mg)M treated (Ca +Mg)M untreated The DVGW certifies a device with an EF greater than 0.8 For this study the EF will be used as a relative measure without applying any pass fail criteria.
  • 24. Waters to be Tested City of Tempe Tap water – Salt River (180 mg/l of hardness as CaCO3) Colorado River Water – Central Arizona Project treated at Scottsdale Water Campus (150-220 mg/L of hardness as CaCO3) Groundwater – South Scottsdale at Pima Park Treatment Facility – Treated by Air Stripping (200-250 mg/L of hardness as CaCO3) Santa Clara/San Jose Sub-basin Groundwater – Completed in California
  • 25. Schedule – Months of Testing at ASU Salt River Water – Three months First Two Runs - No Treatment and Ion exchange Next Four Runs - Four Alternative Treatment Devices Colorado River water – Two months – Four Alternative Treatment Devices South Scottsdale Groundwater – Two months – Four Alternative Treatment Devices Salt River Water – Two Months – Repeat Tests at 60oC
  • 26. RESULTS -Tempe Tap - Untreated
  • 27. Tempe Tap – Template Assisted Crystallization
  • 28. Tempe Tap – Electromagnetic
  • 29. Tempe Tap – Electrically Induced Precipitation
  • 30. Tempe Tap – Capacitive Deionization Almost all scale measured was found in the bath.
  • 31. Results Summary Water Type Treatment device used Scale scraped off of heating element (g) % Ca as CaCO3 in scale forme d Ca formed in solid scale precipitate (g Ca as CaCO3) Scale from bath and heating element dissolved with HCl (g Ca as CaCO3) Total calcium formed during test (g Ca as CaCO3) Photo of heating element with scale Tempe tap water No Treatment - NA 0.0 8.4 8.4 Template Assisted Crystallization 0.0 NA 0.0 0.3 0.3 Electrically Induced Precipitation 0.7 87.2 0.6 3.5 4.1 Electromagnetic 1.4 87.2 1.3 3.6 4.9 Capacitive Deionization 0.0 NA 0.0 1.4 1.4 Ion Exchange
  • 32. Preliminary Results Template Assisted Crystallization worked best Capacitive Deionization worked well enough to pass DVGW test Both Electromagnetic treatment and electrically induced precipitation reduced scale formation significantly. The scale formed was “soft” scale that easily brushed off. The test does not determine long term accumulation
  • 33. A rapid assessment test would be highly desirable Both Template Assisted Crystallization and Electromagnetic Devices might create microscopic forms of CaCO3 that remain suspended Use this fact to develop a rapid assessment test Two possible methods Filtration to separate suspended CaCO3 Hach Kit – EDTA will only measure soluble Ca and Mg Surface Tension, X-ray diffraction, spectroscopy, etc.
  • 34. Results with Hach Kit using Electromagnetic Treatment Tempe Tap Water Total Hardness After Acidification No Treatment 163.2 After Electromagnetic Treatment 123.2 156.8 After Template Assisted Crystallization Treatment 168 167 Langeleir Index with No Treatment = +0.24 Langeleir Index After EM Treatment = -0.08
  • 36. X Ray Diffraction 0 500 1000 1500 2000 2500 3000 3500 4000 4500 5000 10 15 20 25 30 35 40 45 50 55 60 Intensity Angle XRD Magnetic Treatment 0 1000 2000 3000 4000 5000 6000 10 15 20 25 30 35 40 45 50 55 60 Intensity Angle XRD Untreated Both have calcite patterned peaks.
  • 37. RAMAN Spectroscopy RAMAN Spectrum of water Untreated Magnetic Treatment
  • 38. Acceptance??? – not up to Water Reuse Foundation or Researchers IAPMO is developing a standard protocol based on the DVGW – National Sanitation Foundation can then certify Industrial/Commercial applications are strong candidates – understand maintenance issues and desire cost savings Homeowners – depends on green movement and willingness to accept potential problems (Dissolved CO2, etc.)