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Removal of Arsenic from Drinking Water

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ACTION 637: Metals and Related Substances in Drinking Water M E T E A U Removal of Arsenic from Drinking Water by Nanofiltration Zdravka Lazarova – PowerPoint PPT presentation

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Title: Removal of Arsenic from Drinking Water


1
Removal 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

6
Pressure-Driven Membrane Processes

COMPARISON MF - UF NF- RO
7
Source adapted from http//www.kochmembrane.com
8
NF - 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
9
Membrane 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

11
EXPERIMENTS

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
Membrane name Description Salt Rejection Permeability (Lmh/bar) Zeta Potential (mV)
NF270 loose NF 40-60 13 -5 to -16
NF90 tight NF 85-95 6.7 -15 to -30
12
Membrane Test Unit AMAFILTER
Flow Rate 100- 1000 L/h Pressure 0-60
bar Membrane contact surface 63,5 cm2
13
(No Transcript)
14
Comparison NF270-NF200-NF90 permeate flux as a
function of pressure difference
As(V)- As(III) at 400 L/h pH 8
As100µg/LT25C
15
Comparison NF270-NF200-NF90 As-retention as a
function of pressure difference
As(V)- As(III) at 400 L/h pH8
As100µg/LT25C
16
As(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
17
As(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
18
As- Retention/Flux as a function of pH-value
MEMBRANES NF-90
Q 400 L/h pH 8 pressure 5 bar T25C
19
COMPARISON As(V)- Sb(V)

20 bar
15 bar
20 bar
10 bar
15 bar
5 bar
10 bar
5 bar
20
CONCLUSIONS
  • 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

21
Electrochemical Oxidation of As-containing waters
FLOW SHEET DIAGRAMM
H2O
-e-
H OH-
  • ORGANIK

As(III)
mobile electrochemical plant
As(V)
22
Austrian Research Centers GmbH -ARC

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