capacitive deionization (CDI) approach Htet Hte Kyaw - - PowerPoint PPT Presentation

capacitive deionization cdi
SMART_READER_LITE
LIVE PREVIEW

capacitive deionization (CDI) approach Htet Hte Kyaw - - PowerPoint PPT Presentation

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 &


slide-1
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
SLIDE 2

Capacitor

Conducting plate (Al foil) Electrodes Dielectric

+ + + + + + + +

  • +

+ + + + + + +

  • +

Electric double layer Q+ Q- A typical capacitor Dielectric

slide-3
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
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
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
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
SLIDE 7

Capacitive Deionization

+ + + + + + + + + +

  • - - - - - - - - -

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
SLIDE 8

+ + + + + + + + + +

  • Electrode

Electrode Regeneration process

Anion Cation

+ + + + + + + + + +

  • Brine solution (Out)

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
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
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
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
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
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
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
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
SLIDE 16

16

Nanotechnology Research Centre The Research Council of Oman (TRC) Sultan Qaboos University Acknowledgements

slide-17
SLIDE 17

17

CDI prototype