Electrically Conducting Carbon Nanotube - Polymer Composite Membranes for Fouling Prevention David Jassby Department of Chemical and Environmental Engineering
Membrane Fouling Membrane fouling a major problem in water treatment processes Organic/colloidal deposition NOM and polysaccharides (alginic acid) Mineral scaling Kim et al., 2010 Ca CaCO 3 Biofilm formation
Electrofiltration Electrically charged surfaces have been demonstrated to Prevent biofilm growth Slow down/eliminate mineral scale formation Induce electrostatic repulsive forces The challenge: Create an electrically conducting, semi-permeable surface, which maintains the necessary transport properties needed in water treatment processes High salt rejection, high flux, robust, cheap The solution: CNT polymer composites combine the selectivity and flexibility of polymers with the electrical conductivity of CNTs
Electrically Conducting RO Membranes Ester bond linking TMC to hydroxyl group on CNT Contact angle = 77 ± 3 Plain PA
Scaling Inhibition Scaling the formation of salt crystals on the membrane surface Salt concentrations increase along membrane surface (concentration polarization) leading to supersaturated conditions, nucleation and crystal growth Ca (gypsum) scaling is a serious challenge while desalinating certain inland brackish waters Difficult to control due to insensitivity to ph conditions Requires the addition of anti-scaling agents to prevent precipitation
Scaling Inhibition Ca In our experiments: Scaling solution CaCl 2, Mg, Na 2 Ionic strength = 0.134 M Saturation index = 1.01 Cross-flow velocity = 2 cm/s No bulk crystallization outside of membrane module Feed water was recirculated through the membrane module and back to the feed tank with no filtration Voltage applied as DC Three distinct regions on membrane Inlet Area Transition Heavy Scaling
Relative Flux Scaling Inhibition Ca Applying a DC voltage had a significant impact on scale formation Charge sign was determined to be critical for membrane performance Membrane as anode (positive charge) inhibited scaling Membrane as cathode (negative charge) encouraged scaling 1 0.8 0.6 0.4 0.2 1.5 V 0V.5 V -1.5 V 0 75 150 225 300 Time (Min.)
Scaling Inhibition Ca The application of a positive DC potential changed crystal morphology In controls, crystals appear small, needle-like, and tightly packed When membrane is used as an anode (1.5V), crystals are much larger and loosely packed 0 V 1.5 V
Scaling Inhibition Ca The electric double-layer structure forming along the electrically charged membrane surface exhibits nonstoichiometric conditions in the diffuse layer, with regards to Ca 2 and ion concentrations Non-stoichiometric conditions lead to longer induction times Away from the membrane, stoichiometric conditions are re-established and nucleation takes place in the bulk Stoichiometric Mixture Non Stoichiometric Mixture SO 4 Ca 2 Ca 2 Ca 2 Bulk Diffuse Layer Stern Layer R = Ca 2 Alimi and Gadri, Desalination, 2004
Scaling Modeling Ca We use a modified Poisson- Boltzmann equation to predict the potential distribution as a function of distance from the membrane surface We calculate ion concentrations as a function of potential c i = 1 -en d 2 A Y e e dx = 2 m 1 m å i=1 m å i=1 c i max i=1 c i å æ c i exp - z ey ö i ç è kt ø c i é æ exp - z iey ö ù max ê ç -1ú c i ë è kt ø û æ z i c i exp - z iey ö ç è kt ø é æ exp - z iey ö ù ê ç -1ú ë è kt ø û p c max i = 4 3 p R 3 i N A
Organic Fouling on UF Membranes UF Membranes are composed of a PVA-CNT- COOH thin film deposited on a PSF support PVA and COOH (on CNTs) groups cross-linked with gluteraldehyde 100 80 60 40 20 0 35.0 50.0 150.0 200.0 Molecal Weight (kmw) PVA-CNT PS-35 PSF only 49 CNT only 81 PVACNT 32
Organic Fouling on UF Membranes We used high concentrations of alginic acid (5 g/l) as a model organic foulant Cross-flow membrane system operated with constant flux (20 LMH, 10 cm/s) Surface hydrophilicity reduces organic fouling Ionic strength has significant impact of electrostatic repulsion (not surprising) Neutral organic foulants (PEO) are not impacted by electric fields 24 Alginic Acid Alginic Acid WW PEO (neutral) 22 30 22 20 20 18 16 14 12 10 0.0VDC PS-35 0.0VDC PVA-CNT -3.0VDC PVA-CNT -5.0VDC PVA-CNT 8 0 20 40 60 80 100 Time (Minute) Pressure (psi) 18 16 14 12 10-5VDC PVA-CNT 8 0 20 40 60 80 100 Time (Minute) Pressure (psi) 0.0VDC PS-35 0VDC PVA-CNT -3VDC PVA-CNT 25 20 15 10 0.0VDC PS-35 0VDC PVA-CNT -3VDC PVA-CNT -5VDC PVA-CNT 0 20 40 60 80 100 Time (Minute)
Conclusions By combining electrically conducting CNTs with appropriate polymers (such as PA or PVA), membranes can maintain their critical transport properties, e.g. salt rejection and water permeability, with the addition of electrical conductivity Electrically charged membranes can reduce membrane fouling Scaling inhibition on RO membranes Organic fouling (molecules and biofilms) Ionic strength greatly impacts system performance Modeling of electrostatic phenomena in these systems require a different approach (simple DLVO doesn t work)
Acknowledgements UC Riverside Wenyan Duan Alexander Dudchenko Duke University Mark Wiesner Charles de Lannoy