Synthesis of cyclodextrin polyurethane carbon nanotubes composites incorporating alginate for the removal of chemical contaminants in water By H.I. EZURUIKE, Supervisors: PROF.R.W. KRAUSE,PROF.B.B. MAMBA
LAY OUT BACK GROUND OBJECTIVES EXPERIMENTAL & CHARACTERIZATION RESULTS & DISCUSSION CONCLUSIONS ACKNOWLEDGEMENT
BACK GROUND …. Clean water = essential human health + environment Water often contaminated (organic + inorganic). HOW?
BACK GROUND …. Organic contaminants Polycyclic aromatic hydrocarbons ( PAHs ) Aromatic compound such as benzenes,toluene,phenol and their derivatives Polychlorinated biphenyls (PCBs) Endocrine disrupting compounds (EDCs) Inorganic contaminants Lead (Pb), Mercury (Hg), Copper (Cu), Zinc (Zn) and Cadmium
OBJECTIVES Characterize polymer formed using techniques such as Fourier transformed infra red (FT-IR),TEM and (SEM) Incorporate alginates to form beads Test ability of beads to remove desired chemical contaminants.
EXPERIMENTAL METHOD Divided into four (4) distinct parts: 1. The functionalization of carbon nanotubes 2. The polymerization of CD with CNTs using bifunctional linkers to form polymers 3. Making Alginate composites to form beads 4. Model contaminants removal using novel polymers (beads)
The functionalization of carbon nanotubes
The polymerization of CD with CNTs using bifunctional linkers
The polymerization of CD with CNTs using bifunctional linkers (cont…)
Preparation of porous crosslinked β -CD Alginate nano beads
CHARACTERIZATION IR - functional groups SEM/Micrograph pictures - Surface morphology or physical nature solids TEM - View CNTs structure and see if it has formed (multi walled) UV-qualitative and quantitative determination of compounds
RESULTS & DISCUSSION Table 1.1: Yield of MWNTs oxidized at 50 O C for 24 hrs Source of MWNTs Mass before (g) Mass after (g) Yield (%) Commercial MWNTs 1.000 0.880 89 NSP- MWNTs 0.520 0.385 76
RESULTS & DISCUSSION TEM Figure 1: R aw commercial MWNTs
RESULTS & DISCUSSION TEM Figure 2: Raw NSP MWNTs
RESULTS & DISCUSSION TEM Figure 3: NSP MWNTs functionalized at 50 C
RESULTS & DISCUSSION FT-IR Spectroscopy Figure 4: CNTs before functionalization
RESULTS & DISCUSSION IR Spectroscopy Figure 5: IR of CNTs after functionalization
RESULTS & DISCUSSION IR Spectroscopy Figure 6: Polymerization of CD with carbon nanotubes at beginning of rxn
RESULTS & DISCUSSION IR Spectroscopy Figure 7: Polymerization of CD with carbon nanotubes at end of reaction
RESULTS & DISCUSSION Scanning electron microscopy (SEM)
RESULTS & DISCUSSION Freundlich Isotherm Slope= 1.0438=1/n; n=0.9580 Intercept=0.8752=log K; K =0.05 Therefore substitute values in Freundlich equation: log (x/m)=log K +1/n log C
RESULTS & DISCUSSION Contact Time Time (hrs) C (mg/L) C/C (mg/L) 10 0.3426 0.6365 17 0.3643 0.5406 24 0.3760 0.4707 31 0.4205 0.4399 38 0.4905 0.4394 48 0.5520 0.4393
CONCLUSIONS The amount of p-nitrophenol adsorbed onto the polymer beads increased with an increase in time Experimental data fitted to both Langmuir and Freundlich models, R 2 = 0.9546 and 0.8068 respectively Langmuir’s model was a choice because of high R 2 values Equilibrium at 38 hrs (0.44mg/L,76.8% removal) Polymer has great potential to remove p-nitrophenol in water.
ACKNOWLEDGEMENTS University of Johannesburg DST/ Mintek Nanotechnology Innovation Center National Research Foundation (NRF),SA Eskom’s Tertiary Education Support Program My Supervisors for moral support THANK YOU