SLIDE 1
Brackish water desalination using capacitive deionization (CDI) approach
Htet Hte Kyaw Nanotechnology Research Centre Sultan Qaboos University
Seminar on "Small Desalination Units for Agriculture Sustainability, (Challenges & Opportunities)”
SLIDE 2 Capacitor
Conducting plate (Al foil) Electrodes Dielectric
+ + + + + + + +
+ + + + + + +
Electric double layer Q+ Q- A typical capacitor Dielectric
SLIDE 3
Desalination
Desalination grew from 3% of total water supply in 1999 to 13% in 2008 RO desalination is the main desalination technology used
SLIDE 4
Energy Consumption
Energy Requirement RO CDI Electrical (kWh/m3) 2 < 1 Acceptable salinity level for different applications
Irrigation & industrial cooling system – 1000 to 3000 ppm Household use – up to 1000 ppm Safe drinking water – less than 150 ppm Industrial level (high end product) – less than 5 ppm § Only ions can be removed § High energy consumption for high salinity water
Some limitations Main advantages of CDI technology
CDI exhibit less fouling No electrode deterioration No pressure required Less energy
SLIDE 5 Sea Water Intrusion
Well pumping fresh water Salt water Fresh groundwater Ocean Well pumping salty water Sea water intrusion Cone of depression
- 65% of fresh water (ground water) available in Oman
- Increased demand combined with falling water tables lead
to rapid seawater intrusion.
After pumping by many wells
SLIDE 6 (Oman Salinity Strategy. In Ministry Of Agriculture And Fisheries: Sultanate of Oman, 2012)
Sea Water Intrusion
- Al Batinah region accounts
for >50% of Oman’s agriculture
- Rapid population growth &
increased agricultural activities
- Salinity increased due to
sea water intrusion
2,000 km of coastline
SLIDE 7 Capacitive Deionization
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Electrode Electrode
Saline water Electrochemical controlled technique to remove ions by applied potential Higher surface area Higher ions adsorption Anion (Cl -) Cation (Na +) Electrosorption process
Desalination process
200 400 600 800 1000 1200 0.05 0.10 0.15 0.20 0.25
conductivity (mS/cm)
time (s)
SLIDE 8 + + + + + + + + + +
Electrode Regeneration process
Anion Cation
+ + + + + + + + + +
Capacitive Deionization
Higher surface area Higher ions adsorption Electrosorption process
1400 1600 1800 2000 2200 2400 2600 2800 3000 0.05 0.10 0.15 0.20 0.25 0.30
conductivity (mS/cm)
time (s)
SLIDE 9 CDI cell structure
100 m
Current collector Acrylic plate Activated carbon cloth Activated carbon cloth Spacer Acrylic plate Current collector Inlet Outlet
Specific surface area – 1043 m2/g pore volume – 1.417 cm3/g Mean pore diameter – 0.7 nm & total pore volume – 1.417 cm3/g
FM-100 ACC Zorflex
SLIDE 10
Results
► Synthetic Brackish water – 1, 3 and 5 g/l ► Desalination cycle – 17 min
Effect of salt concentration on desalination by synthetic water
► Feed water salinity increased Desalination efficiency decreased ► Rate of salt adsorption increased
SLIDE 11
Synthetic water Vs Brackish water (from a well in Al Musanaah)
Results
Sample Desalination efficiency (%) Power consumption (kWh/m3) Electrode salt adsorption capacity (mg/g) Synthetic water 32 0.85 10.5 mg/g Well water 27 0.75 8.9 mg/g
SLIDE 12 Ion Selectivity
Results
- Divalent species like Ca2+ preferentially adsorb over the monovalent
species
- Higher K+ removal efficiency due to lower concentration in well water
SLIDE 13 Results
Disinfection properties
Bacterial electroadsorption on ACC surface
Electrode surface creates a hypertonic environment Dehydration of cells lead to cell death 3-fold reduction in bacterial colonies after desalination Electroadsorption is dominant mechanism
- f disinfection
- K. Luxman et al., Desalination 362 (2015) 126-132
SLIDE 14 14
Results
- Desalination trends over a period of 1 day for brackish water and synthetic
water of similar conductivity
- 0.01 M citric acid (pH 2.96) followed by 0.01 M NaOH cleaning after 24
hours of operation
Long term desalination and electrode regeneration
SLIDE 15 15
Conclusions
- Brackish water was successfully treated using CDI
- Brackish water power consumption was marginally lower
(0.78 kWh/m3) compared to synthetic water (0.85 kWh/m3)
- Disinfection properties mainly attributed to
electroadsorption of microbes
- Scale forming ions (Ca2+) is efficiently removed during the
process
- Electrodes were completely regenerated after cleaning
leading to repeatable desalting capabilities
SLIDE 16 16
Nanotechnology Research Centre The Research Council of Oman (TRC) Sultan Qaboos University Acknowledgements
SLIDE 17 17
CDI prototype