Title: Removal of Arsenic from Drinking Water
1Removal of Arsenic from Drinking Water by
Nanofiltration
Zdravka Lazarova Austrian Research Centers GmbH
ARC Department WATER
2- Outline
- Pressure-Driven Membrane Processes
- Nanofiltration Main Characteristics
- Experimental Results on NF of As(III) and
As(V) - Comparison NF90, NF200, NF270
- Effect of Process Parameters
- pressure difference
- arsenic concentration
- pH value of feed
- Conclusions
3- Arsenic Removal Technologies for Drinking Water
Treatment - VIABLE TREATMENT TECHNOLOGIES
- Coagulation Precipitation
- Adsorption
- Ion Exchange
- Oxidation
- Biological Techniques
- MEMBRANE SEPARATIONS
-
4 - Arsenic Removal Technologies for Drinking Water
Treatment - Best Available Technologies (BAT) for Arsenic
removal ? -
- USEPA suggested for As(V)
- Ion exchange
- Activated alumina
- Reverse osmosis
- Coagulation/filtration
- Lime softening
5 - Arsenic Removal Technologies for Drinking Water
Treatment - Technologies with increasing importance !
- Granular Ferric Hydroxide (GFH)
- Iron-based Coagulation/Microfiltration
- Iron Oxide-Coated Sand
- NANOFILTRATION
6Pressure-Driven Membrane Processes
COMPARISON MF - UF NF- RO
7Source adapted from http//www.kochmembrane.com
8NF - Process Characteristics
- Performance characteristics between RO and UF
- Essentially lower pressure than RO (P 0.5-6
MPa) - Removes molecules in the 0.001 µm range (MWCO
0.2 to 200) - Applications water softening, removing of
organic matter, desalting of organic reaction
products, removal of nitrates, removal of metal
ions
Source adapter from http//www.kochmembrane.com
9Membrane Process Applied for Large-Scale
Cross-Flow Membrane Filtration
R(C)
RETENTATE (As-Concentrate)
Feed
?p
PERMEATE (pure water)
P
10- SOLUTION CHEMISTRY
- pH
- As-concentration
- As-species
- Ionic strength
- Co-solutes
- FUNCTIONAL PHYSICAL PARAMETERS
- Pressure
- Temperature
- Flow Rate (cross-flow velocity)
- Recovery
- MEMBRANE CHARACTERISTICS
- Porosity/MWCO
- Charge
- Salt separation ability
- Hydrophilicity
- Fouling
11EXPERIMENTS
COMPARISON performance of NF90, NF200, NF270 for
removal of As(III) and As(V) from drinking water
- Effect of pressure difference
- Effect of pH
- Effect of As-concentration
FilmTec TM NF Membranes, Dow, USA
12Membrane Test Unit AMAFILTER
Flow Rate 100- 1000 L/h Pressure 0-60
bar Membrane contact surface 63,5 cm2
13(No Transcript)
14Comparison NF270-NF200-NF90 permeate flux as a
function of pressure difference
As(V)- As(III) at 400 L/h pH 8
As100µg/LT25C
15Comparison NF270-NF200-NF90 As-retention as a
function of pressure difference
As(V)- As(III) at 400 L/h pH8
As100µg/LT25C
16As(V) -retention as a function of
As-concentration in feedMEMBRANES NF-90
NF-270 (T)
Q 400 L/h pH 8 pressure 5 bar T25C
17As(III) -retention as a function of
As-concentration in feedMEMBRANES NF-90
NF-270 (T)
Q 400 L/h pH 8 pressure 5 bar T25C
18As- Retention/Flux as a function of pH-value
MEMBRANES NF-90
Q 400 L/h pH 8 pressure 5 bar T25C
19COMPARISON As(V)- Sb(V)
20 bar
15 bar
20 bar
10 bar
15 bar
5 bar
10 bar
5 bar
20CONCLUSIONS
- COMPARISON NF-MEMBRANES NF-90, NF-200, NF270
- Membrane performance depends on arsenic forms
(As(III) As(V)) and experimental conditions
(feed concentration, pH, ionic strength?, feed
matrix (co-ions )? - Arsenic retention efficiency follows the order
NF90gtNF200gtNF270 - Removal of As(V) is substantially higher not
sensitive to pressure changes (96-99 at 5-20
bar) - Effect of feed concentration on As- rejection
depends on the membrane type - As(III) treatment is more sensitive to the
pH-value of the feed - Pilot experiments are needed for process
optimisation
21Electrochemical Oxidation of As-containing waters
FLOW SHEET DIAGRAMM
H2O
-e-
H OH-
As(III)
mobile electrochemical plant
As(V)
22Austrian Research Centers GmbH -ARC
Thank you for your attention