Micro- and Nanosized TiO 2 Particles Immobilized in Sintered - - PowerPoint PPT Presentation

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Micro- and Nanosized TiO 2 Particles Immobilized in Sintered - - PowerPoint PPT Presentation

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


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Micro- and Nanosized TiO2 Particles Immobilized in Sintered Recycled Glass for the Degradation of THM Precursors in Surface Waters

Pedro J. Tarafa1, Sheila Arias1, Leroy Goñez2 and Marcelo Suarez3

  • 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

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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)

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SLIDE 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)

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Goal

Develop a porous filter-like composite made out of glass to support titanium dioxide (TiO2) micro- and nanoparticles as a low cost alternative for the destruction of THM precursors

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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 TiO2 particles within the glass matrix

in order to make a TiO2-glass composite.

  • 4. Observe the polymorph structure of TiO2 for the selected

sintering temperatures by x-ray diffraction analysis (XRD).

  • 5. Evaluate

the glass-TiO2 composite capacity for the degradation of humic acid under the influence of UV light by means of total organic carbon (TOC) analyses.

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Methodology

Parameters under evaluation:

  • 1. Sieve analysis for the crushed glass
  • 2. Structural analyses for the glass /TiO2 composites
  • Percolation
  • Surface porosity
  • 3. Mechanical analyses for the glass/TiO2 composites
  • Compression
  • 4. XRD analysis for the TiO2
  • 5. Humic acid degradation potential

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Methodology (cont.)

Glass substrates and glass-TiO2 composite preparation: Final Glass/TiO2 sample 950 -1,000˚C 45 -75 minutes Muffle furnace Ceramic mold

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Methodology (cont.)

Percolation:

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Methodology (cont.)

Photo-degradation reactor box:

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Results

Sieve analysis for the crushed glass:

10 20 30 40 50 60 70 80 90 100

0.01 0.10 1.00 10.00

Percent Passing by Weight Sieve Opening (mm)

Effective Size (d10): 0.47 mm Finer Size (d60): 0.74 mm Uniformity Coefficient (UC): 1.57

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Results (cont.)

Percolation data for the sintered glass substrates with time and temperature: Sintering temperature (oC) Sintering time (min) Average Percolation flux (gpm/ft2) 950 45 17.71 60 15.58 75 12.06 975 45 9.01 60 7.06 75 3.64 1000 45 5.59 60 0.17 75 0.059

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Results (cont.)

Percolation data for the glass-TiO2 composites with time and temperature: Sintering temperature (oC) Sintering time (min) Average Percolation flux (gpm/ft2) 950 60 36.20 75 32.83 90 27.88 975 60 25.85 75 15.36 90 12.66

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Results (cont.)

TiO2 XRD spectrum: Characteristic peak for TiO2 anatase phase

Operations: Import 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

Lin (Counts)

1000 2000 3000 4000 5000

2-Theta - Scale

15 20 30 40 50 60 70

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Results (cont.)

XRD spectra for TiO2 at different temperatures:

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Results (cont.)

XRD spectra for TiO2 + ethanol at different temperatures:

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Results (cont.)

XRD spectra for glass-TiO2 composites: 975oC 950oC

SGS = sintered glass substrate

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Results (cont.)

TiO2 deposition into the glass powder sintered at 750oC for

  • 25min. (a) 0% of TiO2 at 500 μm (b) 1.0% of TiO2 at 500μm

(c) 1.0% of TiO2 at 100μm Scanning Electron Microscope (SEM)

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Results (cont.)

0.9 1.0 1.1 10 20 30 40 50 60 70 80

TOC/TOC0 Irradiation Time (min)

Degradation of humic acid with TiO2-glass composites under the influence of UV light

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Results (cont.)

Degradation with TiO2 and TiO2 mixtures suspensions at different temperatures under the influence of UV light

0.00 0.20 0.40 0.60 0.80 1.00 20 40 60 80 100 120 140

[Ci]/[C0] Time (min) TiO2 TiO2 + EtOH TiO2 + EtOH @ 950oC TiO2 @ 950oC

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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 TiO2

particles.

  • Filtration rates similar to those found for traditional rapid sand

filters can be achieved.

  • The anatase phase in TiO2 remains after exposure to high

temperatures for glass sintering.

  • The TiO2 particles have photo-activation capacity, even after

been exposed to the chemicals and temperatures for glass sintering.

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Summary and Conclusions

  • The optimal amount of TiO2 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 TiO2 most likely due to low UV light penetration through the glass composite.

  • Results are promising provided that TiO2 is favored to promote

photo-degradation, however, alternate immobilization methods for the TiO2 that could yield in higher UV exposure for higher photo-degradation should be evaluated.

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On-going and future work

  • Surface porosity of the sintered glass and glass/TiO2

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 TiO2 in the glass substrate by deposition of TiO2 suspension over the sintered glass surface coating the sintered glass surface. a. Using EtOH + nitric acid, and

  • b. polyvinyl alcohol

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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

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