partitioning of inorganic contaminants into the polyamide active layers of thin-film composite...
TRANSCRIPT
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Partitioning of Inorganic Contaminants into the Polyamide Active Layers of Thin-film Composite
Membranes for Water Purification
Jingbo Wang, Lamar A. Perry, Orlando CoronellDepartment of Environmental Sciences and Engineering
University of North Carolina at Chapel Hill
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Background
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RO/NF Membrane structure
Polyamide ~20-200 nm
Polysulfone ~30-50 μm
Background
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Polyester ~40-100 μm
Active layer
Support layers
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RO/NF Membrane structure
Polyamide ~20-200 nm
Polysulfone ~30-50 μm
Background
4
Polyester ~40-100 μm
Active layer
Support layers
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Solution-diffusion modelBackground
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Feed water
Permeate
Membrane active layer
NaCl partition
partition
diffusion
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Solution-diffusion modelBackground
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𝑩=𝑫𝑲 /𝜹𝒎
𝑱 𝒔=𝑩 ∙∆𝑪
Diffusion coefficient Partition coefficient
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Membrane rejection can be as high as 99.95%
Study Mi et al Zhang et al Kotelyanskii et al
Partitioning solute arsenic(III) CsCl, KBr
Membrane type Thin film composite FT30
Technique RBS RBS Atomistic modeling
Partition coefficient 6±2 3.6~8.1 estimation~2
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Partition coefficients in literatureBackground
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To develop a simple and accurate method for measuring the partition coefficient of inorganic solutes between aqueous solution and polyamide active layers of RO/NF membranes.
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Objective
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Materials and Methods
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Quartz Crystal Microbalance (QCM)
Materials and methods
Constant water/solution flow
Isolated active layer (AL)
QCM sensor
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NaClNaCl
NaCl
QCM sensor QCM sensor
Membrane active layer
SolutionWater
Quartz Crystal Microbalance (QCM)
Materials and methods
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Partition coefficientMaterials and methods
K =
CM: solute concentration in membrane, M
Cs : solute concentration in solution, M
Obtain from QCM
CM
Cs
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Membranes and solutesMaterials and methods
Membrane
SWC4+ (seawater RO), ESPA 3(brackish water RO) ,
XLE (brackish water RO), NF90 (nanofiltration)
Solutes
Alkali metal chlorides, Boric acid
Concentration range
0.001M-1M
pH=5.3
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Results
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QCM raw dataResults
water
0.001M NaCl
water
0.01M NaCl
0.1M NaCl
0.4M NaCl
1.0M NaCl
2 ControlSample
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Data analysis – membrane chargeResults
Na+Cl-
Cl-
--
Na+ Membrane active layer-
- -Na+Na+ Na+
Na+
Cl-
Cl-
Cl-
Na+ Cl-
Cl- Cl-Cl-
Cl- Cl-
Cl-Na+
Na+ Na+Na+ Na+
Na+
Cl-
- -
Increasing mass= ion neutralizing fixed charge + partitioning solute
Na+Na+
Na+Cl-
Na+ Na+
Cl- Cl-
Na+ Na+
Na+Na+Cl-Cl-
Cl-
Cl-
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Baseline of data analysisResults
water
0.001M NaCl
water
0.01M NaCl
0.1M NaCl
0.4M NaCl
1.0M NaCl
2 ControlSample
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0 0.2 0.4 0.6 0.8 10
150
300
450
600
NaCl KCl
Boric acid
Cs (M)
CM
(ng/
cm2)
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0 0.2 0.4 0.6 0.8 10
150
300
450
600
NaCl KCl
Boric acid
Cs (M)
CM
(ng/
cm2)
K =CM
Cs
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Data analysisResults
Mass reading from QCM = weight of partitioning solutes, ng/cm2
Unit conversion from ng/cm2 to M
CM: solute concentration in membrane, M
Cs : solute concentration in solution, M
K =CM
Cs
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QCM sensorQCM sensor
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NaCl·xH2O
NaCl
Scenario D
Hydrated solute
partitioning+
Membrane dehydration
QCM sensor
NaCl
NaCl
NaCl
NaCl
H2O
NaCl·xH2O NaCl·xH2O
QCM sensor
NaCl·xH2O
NaCl·xH2O H2O
Scenario C
Non-hydrated solute
partitioning+
Membrane dehydration
Scenario B
Hydrated solute
partitioningonly
Scenario A
Non-hydrated solute
partitioning only
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Partition coefficientResults
0 0.2 0.4 0.6 0.8 10
0.2
0.4
0.6 KCl
Cs (M)
CM
(M) K = 0.64
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Scenario Hydrated solute?
Membrane dehydration?
K
KCl NaCl H3BO3
A No No 0.64 0.63 0.54
B Yes No 0.48 0.31 –
C No Yes 0.82 0.86 –
D Yes Yes 1.17 0.90 –
Table.1. A summary of partition coefficients obtained with SWC4+ membrane at pH=5.3
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Partition coefficientResults
This study(QCM)
Previous studies(RBS)
Partition coefficient 0.31~1.17 3.6~8.1
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Conclusion
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Conclusion
1. We successfully developed a bench top method to measure solute partition coefficients using a QCM as an analytical tool.
2. The partition coefficients of chloride salts of all alkali metals and of the weak acid studied were all lower than or very close to 1.
3. The results are not in agreement with the results obtained using RBS as an analytical tool in which the partition coefficients of inorganic salts and arsenious acid were reported to be in the 3.6 to 8.1 range.
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Future Work
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Future work
𝑱 𝒔=𝑫𝑲 ∙∆𝑪 /𝜹𝒎
Diffusion coefficient Partition coefficient
Solute fluxConcentration
gradientActive layer thickness
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Acknowledgment
• Funding sources
• Coronell research group
Lin Lin
• National Science Foundation (NSF) Grants Opportunities for Academic Liaison with Industry (GOALI) and Chemical and Biological Separations programs under Award#1264690
• NSF Environmental Engineering program under Award#1336532.
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References cited
[1] Freger, V., & Ben-David, A. Use of attenuated total reflection infrared spectroscopy for analysis of partitioning of solutes between thin films and solution. Analytical chemistry, 2005, 77(18), 6019-6025.[2] Ben-David, A., Oren, Y., & Freger, V. Thermodynamic factors in partitioning and rejection of organic compounds by polyamide composite membranes. Environ. Sci. Technol. 2006, 40(22), 7023-7028.[3] Geise, G. M., Falcon, L. P., Freeman, B. D., & Paul, D. R.. Sodium chloride sorption in sulfonated polymers for membrane applications. Journal of Membrane Science, 2012, 423, 195-208.[4] Lonsdale, H. K., Merten, U., & Riley, R. L.. Transport properties of cellulose acetate osmotic membranes. Journal of Applied Polymer Science, 1965, 9(4), 1341-1362.[5] Mi, B., Mariñas, B. J., & Cahill, D. G. RBS characterization of arsenic (III) partitioning from aqueous phase into the active layers of thin-film composite NF/RO membranes. Environ. Sci. Technol. 2007, 41(9), 3290-3295.[6] Zhang, X., Cahill, D. G., Coronell, O., & Mariñas, B. J. Partitioning of salt ions in FT30 reverse osmosis membranes. Applied Physics Letters, 2007, 91(18), 181904.[7] Kotelyanskii, M. J.; Wagner, N. J.; Paulaitis, M. E. Atomistic simulation of water and salt transport in the reverse osmosis membrane FT-30. J. Membr. Sci. 1998, 139, 1–16.[8] Sauerbrey, G. (1959). Verwendung von Schwingquarzen zur Wägung dünner Schichten und zur Mikrowägung. Zeitschrift für physik, 155(2), 206-222.[9] Perry, L. A., & Coronell, O. Reliable, bench-top measurements of charge density in the active layers of thin-film composite and nanocomposite membranes using quartz crystal microbalance technology. J. Membr. Sci. 2013, 429, 23-33.