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Micro- and Nanosized TiO 2 Particles Immobilized in Sintered Recycled Glass for the Degradation of THM Precursors in Surface Waters Pedro J. Tarafa 1 , Sheila Arias 1 , Leroy Goez 2 and Marcelo Suarez 3 1. Dept. of Civil Engineering, Univ. of


  1. Micro- and Nanosized TiO 2 Particles Immobilized in Sintered Recycled Glass for the Degradation of THM Precursors in Surface Waters Pedro J. Tarafa 1 , Sheila Arias 1 , Leroy Goñez 2 and Marcelo Suarez 3 1. Dept. of Civil Engineering, Univ. of P. Rico at Mayagüez 2. Dept. of Chemical Engineering, Univ. of P. Rico at Mayagüez 3. Dept. of Eng. Sci and Materials, Univ. of P. Rico at Mayagüez 1

  2. Overview 1. Trihalomethanes • Disinfection by-products that result from the reaction of chlorine with natural organic matter (NOM) present in the water • They are carcinogens • MCL (USEPA) ≤ 80 ppb (0.08 µg/L) 2

  3. Overview (cont.) 2. Strategies for THM Control 1. THM removal by aeration, adsorption or ion exchange processes 2. THM prevention • Changes in chlorination application • Reduction of chlorine doses • Change disinfectant agent • NOM removal (destruction or oxidation) 3

  4. Goal Develop a porous filter-like composite made out of glass to support titanium dioxide (TiO 2 ) micro- and nanoparticles as a low cost alternative for the destruction of THM precursors 4

  5. Specific Objectives 1. Identify an appropriate sintering temperature and time range to obtain a solid, porous glass substrate. 2. Access important thermo-mechanical properties of the glass substrate to support water percolation and strength. 3. Effectively immobilize TiO 2 particles within the glass matrix in order to make a TiO 2 -glass composite. 4. Observe the polymorph structure of TiO 2 for the selected sintering temperatures by x-ray diffraction analysis (XRD). 5. Evaluate the glass-TiO 2 composite capacity for the degradation of humic acid under the influence of UV light by means of total organic carbon (TOC) analyses. 5

  6. Methodology Parameters under evaluation: 1. Sieve analysis for the crushed glass 2. Structural analyses for the glass /TiO 2 composites • Percolation • Surface porosity 3. Mechanical analyses for the glass/TiO 2 composites • Compression 4. XRD analysis for the TiO 2 5. Humic acid degradation potential 6

  7. Methodology (cont.) Glass substrates and glass-TiO 2 composite preparation: Ceramic mold 950 - 1,000˚C 45 -75 minutes Final Glass/TiO 2 sample Muffle furnace 7

  8. Methodology (cont.) Percolation: 8

  9. Methodology (cont.) Photo-degradation reactor box: 9

  10. Results Sieve analysis for the crushed glass: 100 90 Percent Passing by Weight 80 70 60 50 40 30 20 10 0 10.00 1.00 0.10 0.01 Sieve Opening (mm) Effective Size (d 10 ): 0.47 mm Finer Size (d 60 ): 0.74 mm Uniformity Coefficient (UC): 1.57 10

  11. Results (cont.) Percolation data for the sintered glass substrates with time and temperature: Sintering Sintering time Average temperature (min) Percolation flux ( o C) (gpm/ft 2 ) 45 17.71 950 60 15.58 75 12.06 45 9.01 60 7.06 975 75 3.64 45 5.59 1000 60 0.17 75 0.059 11

  12. Results (cont.) Percolation data for the glass-TiO 2 composites with time and temperature: Sintering Sintering time Average temperature (min) Percolation flux ( o C) (gpm/ft 2 ) 60 36.20 75 32.83 950 90 27.88 60 25.85 75 15.36 975 90 12.66 12

  13. Results (cont.) TiO 2 XRD spectrum: Characteristic peak for TiO 2 anatase phase 5000 4000 Lin (Counts) 3000 2000 1000 0 15 20 30 40 50 60 70 2-Theta - Scale Sample: A - File: Sheila-2015-5-6-A.RAW - Type: 2Th/Th locked - Start: 15.000 ° - End: 75.000 ° - Step: 0.020 ° - Step time: 1. s - Temp.: 25 °C (Room) - Time Started: 16 s - 2-Theta: 15.000 ° - Theta: 7.5 Operations: Import 13

  14. Results (cont.) XRD spectra for TiO 2 at different temperatures: 14

  15. Results (cont.) XRD spectra for TiO 2 + ethanol at different temperatures: 15

  16. Results (cont.) XRD spectra for glass-TiO 2 composites: 950 o C 975 o C SGS = sintered glass substrate 16

  17. Results (cont.) Scanning Electron Microscope (SEM) TiO 2 deposition into the glass powder sintered at 750 o C for 25min. (a) 0% of TiO 2 at 500 μ m (b) 1.0% of TiO 2 at 500 μ m (c) 1.0% of TiO 2 at 100 μ m 17

  18. Results (cont.) Degradation of humic acid with TiO 2 -glass composites under the influence of UV light 1.1 TOC/TOC0 1.0 0.9 0 10 20 30 40 50 60 70 80 Irradiation Time (min) 18

  19. Results (cont.) Degradation with TiO 2 and TiO 2 mixtures suspensions at different temperatures under the influence of UV light 1.00 0.80 TiO 2 [Ci]/[C0] 0.60 TiO 2 @ 950 o C TiO 2 + EtOH 0.40 TiO 2 + EtOH @ 950 o C 0.20 0.00 0 20 40 60 80 100 120 140 Time (min) 19

  20. Summary and Conclusions •Temperature and time affect the percolation rate; at higher values of sintering parameters less percolation rate. •The percolation rates was higher in the composites with TiO 2 particles. •Filtration rates similar to those found for traditional rapid sand filters can be achieved. •The anatase phase in TiO 2 remains after exposure to high temperatures for glass sintering. •The TiO 2 particles have photo-activation capacity, even after been exposed to the chemicals and temperatures for glass sintering. 20

  21. Summary and Conclusions • The optimal amount of TiO 2 particles that can be hold for the glass composite is 0.30 g. • The low degradation rate of humic acid indicates low photo- activation of TiO 2 most likely due to low UV light penetration through the glass composite. • Results are promising provided that TiO 2 is favored to promote photo-degradation, however, alternate immobilization methods for the TiO 2 that could yield in higher UV exposure for higher photo-degradation should be evaluated. 21

  22. On-going and future work • Surface porosity of the sintered glass and glass/TiO 2 composite. • Compression analyses. • Examine the adsorptive capacity of the sintered glass for HA. • Perform quantitative and qualitative comparisons on different methods for the immobilization of TiO 2 in the glass substrate by deposition of TiO 2 suspension over the sintered glass surface coating the sintered glass surface. a. Using EtOH + nitric acid, and b. polyvinyl alcohol 22

  23. Acknowledgements • Puerto Rico Water Resources and Environmental Research Institute • USDA – NIFA Center for Education and Trainings in Agriculture and Related Science (CETARS) under grant Nº 2011-38422-30835 • UPRM Department of Civil Engineering and Surveying • Graduate students Sheila Arias and Amarillys Avilés • Undergraduate students Leroy Goñez and José Colón • Drs. Marcelo Suárez, Sangchul Hwang and Félix Román 23

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