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The International Istanbul Textile Congress 2013
May 30th to June 1th 2013, Istanbul, Turkey
1
PHOTOCATALYTIC ACTIVITY OF TIO2 NANOFIBERS FABRICATED
FROM POLYVINYL ACETATE (PVAC)
F. MEMARIAN1
, M. AMANI TEHRAN1
, M. LATIFI2
1
Textile Engineering Department, Amirkabir University of Technology, Tehran, Iran
2
Textile Excellence & Research Centers, AmirKabir University of Technology, Tehran, Iran
fmemariyan@aut.ac.ir
Abstract: Electrospinning of TiO2 nanofibers is remarkably reported in the last decade. It is because of its
high surface to volume ratio which makes it a good choice for catalytic activities. We have used PVAc to
fabricate TiO2 nanofibers using Titanium tetra isopropoxide in the sol gel process with the aid of Acetic Acid
to control hydrolysis reaction of the solution. Electrospinning is performed by choosing a proper feed rate,
High voltage value and distance of nozzle to the collector. Process is continued till a thick layer of nanofiber
webs are achieved and then calcined at 450 c for 3 hours to attain anatase phase of TiO2. The obtained
web has enough strength and flexibility to be lifted gently by clamp. 6 mg of the catalyst was able to degrade
10 ppm Rhodamine B solution throughly in almost 6 hours under UV irradiation. The catalysts preserve its
shape after the 6 hours test when it is electrospun by PVAc..
Keywords: electrospinning; TiO2 nanofibers; photocatalytic activity; PVAc
1. Introduction
Titania is a wide bandgap semiconductor with many interesting properties, such as transparency to visible
light, high refractive index, low absorption coefficient and catalysis[1]. One-dimensional nanostructures of
Titania have been a subject of intense research because of their high specific surface area which makes
them a good choice to purify waste water[2, 3].
Webs of TiO2 nanofibers have been electrospun in different research works using different auxiliary polymers
like Polyvinyl pyrrolidone(PVP)[4-6] and polyvinyl acetate(PVAc)[2, 3, 7]. Ethanol is used as the polymer
solvent in the solution. A titanium sol is used in the solution to attain pure TiO2 in the final product after heat
treatment of nanofibers. The obtained nanofibers are brittle. Therefore for good ability of the catalyst to
degrade the water pollutants to organic materials, a powder of nanofibers are dispersed in waste water using
sonication. Thus a centrifuge stage is needed to remove the nanofibers from the water.
In this paper we have presented the best ratios of materials in electrospinning process to attain TiO2
nanofibers. These solution ratios will be sufficient for fabricating TiO2 in other structures like yarn which can
mentain its structure after heat setting. The purpose of this study is to have a photocatalysis test without a
sonication and centrifuge step. The reuseability of the catalyst will be in the long-term application.
Photocatalysis tests are performed using Rhodamine B(RhB) as a model pollutant.
2. Materials
PVAc (sigma-aldrich) with Mw=100000 is the polymer used in this paper. From different solvents of PVAc
ethanol was the best solvent in electrospinning of nanofibers. Glacial Acetic acid (sigma-aldrich) is used to
prevent hydrolyzing Titanium sol. Titanium tetra iso propoxide (TTIP 97%, sigma Aldrich) is used as a
titanium sol in the solution.
2.1 Method
0.17 gr of PVAc is solved in 1 cc of ethanol and stirred for 10 hours. Then 0.5 cc of acetic acid is added to
the solution with stirring for 15 min. Then TTIP is added to the solution and then it is stirred for another 30
hours. The solution becomes milky when it is ready to electrospin.
Electrospinning is carried out by setting the distance between the nozzle to collector to 9 cm, feeding rate of
0.2 ml/hr and High voltage of 13 KV.
The International Istanbul Textile Congress 2013
May 30th to June 1th 2013, Istanbul, Turkey
2
Electrospun nanofibers need to be annealed for 450 c for 3 hours. During this process, remained polymer
and solvents are omitted from the electrospun nanofibers. Furthermore the amorph TiO2 is converted to the
anatase crystalline phase of TiO2.
The photocatalytic activities of TiO2 nanofibers were investigated by an analysis of the degradation of dyes
under UV illumination. 6 mg of pure TiO2 nanofibers were placed in a glass dish. Then dye solution with the
concentration of 10 ppm was poured on catalyst. This dish is then settled in an aluminium enclosed cell
(17cm×25cm×10 cm). UV irradiation was provided by three 6W light bulb (6W×3) on top of the dish. The
changes in the solution colour show the degradation of dye in the water solution.
2.2 Characterization
The nanofiber samples were sputter- coated with gold (SC7620, Quorum Technologies) and their
morphology was studied with a scanning electron microscope (Philips XL30) at an accelerating voltage of 25
kV. Analysis of the crystalline structures after heat treatment was performed by XRD diffractometer (X'pert
Philips) with Cu Kα radiation (λ=0.15406 nm) in 2Ө range from 10˚ to 80˚ by 0.03˚ sec-1 steps.
3. Results
SEM image of the fabricated nanofibers before and after heat treatment is shown in figure 1. The diameter of
the nanofibers is calculated using image j software. The fibers have an average diameter of 220-280 nm
when they are electrospun. The nanofibers diameter is reduced to 170-180 nm after heat treatment in 450 c
for 3 hours.
Figure 1. electrospun PVAc/TiO2 hybrid nanofiber (left), TiO2 nanofibers after heat treatment at 450 c for 3 hours(right)
As it is clear from the XRD pattern in figure 2, the crystalline TiO2 in anatase phase appears by heating at
450 °C for 3 hours.
Figure 2. XRD image of electrospun nanofibers
Figure 3a shows the initial dye solution on the catalyst sample without UV irradiation. Photocatalytic
degradation of organic dye with UV irradiation after 5 hours is indicated in figure 3b. It is clear that most of
The International Istanbul Textile Congress 2013
May 30th to June 1th 2013, Istanbul, Turkey
3
the dye has been degraded in the catalyst dish. After 6 hours of UV irradiation it was found that 6 mg of the
catalysts is able to disintegrate dye with 10ppm concentration from the water.
Figure 3. dye degradation of the photocatalyst after (a)0 hr-start, (b) 5hr, (c) 6hr
4. Conclusion
PVAc is used as the auxiliary polymer for electrospinning of pure TiO2 nanofibers. The heat treated fibers
were able to be moved in the petri dish. Dye solution has been poured on the catalyst so that powdering the
catalyst is not necessary and it eliminates the need for sonication and centrifuge step in dye degradation.
This method can be promoted by putting the catalyst in a gradient to the horizon, and recycle dye solution to
pass through the catalyst several times.
Fabricating the TiO2 structure with sufficient strength makes it possible to use the catalyst in water without
dispersing it.
References
[1] HASHIMOTO, K., H. IRIE, and A. FUJISHIMA, TiO2 Photocatalysis : A Historical Overview and
Future Prospects. Japanese Journal of Applied Physics, 2005. 44(12): p. 8269-8285.
[2] Doh, S.J., et al., Development of photocatalytic TiO2 nanofibers by electrospinning and its
application to degradation of dye pollutants. Journal of Hazardous Materials, 2008. 154: p. 118-127.
[3] Hamadanian, M., A. Akbari, and V. Jabbari, Electrospun Titanium Dioxide Nanofibers: Fabrication,
Properties and Its Application in Photo-Oxidative Degradation of Methyl Orange (MO). Fibers and
Polymers, 2011. 12(7): p. 880-885.
[4] Li, H., W. Zhang, and W. Pan, Enhanced Photocatalytic Activity of Electrospun TiO2 Nanofibers with
Optimal Anatase/Rutile Ratio. J. Am. Ceram. Soc., 2011: p. 1-4.
[5] Li, D. and Y. Xia, Fabrication of Titania Nanofibers by Electrospinning. Nano letters, 2003. 3(4): p.
555-560.
[6] Watthanaaruna, J., V. Pavarajarna, and P. Supaphol, Titanium (IV) oxide nanofibers by combined
sol–gel and electrospinning techniques: preliminary report on effects of preparation conditions and
secondary metal dopant. Science and Technology of Advanced Materials, 2005. 6: p. 240-245.
[7] Wu, N., et al., Characterization of PVAc/TiO2 Hybrid Nanofibers: From Fibrous Morphologies to
Molecular Structures. Journal ofApplied Polymer Science, 2009. 112: p. 1481-1485.

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  • 1. The International Istanbul Textile Congress 2013 May 30th to June 1th 2013, Istanbul, Turkey 1 PHOTOCATALYTIC ACTIVITY OF TIO2 NANOFIBERS FABRICATED FROM POLYVINYL ACETATE (PVAC) F. MEMARIAN1 , M. AMANI TEHRAN1 , M. LATIFI2 1 Textile Engineering Department, Amirkabir University of Technology, Tehran, Iran 2 Textile Excellence & Research Centers, AmirKabir University of Technology, Tehran, Iran fmemariyan@aut.ac.ir Abstract: Electrospinning of TiO2 nanofibers is remarkably reported in the last decade. It is because of its high surface to volume ratio which makes it a good choice for catalytic activities. We have used PVAc to fabricate TiO2 nanofibers using Titanium tetra isopropoxide in the sol gel process with the aid of Acetic Acid to control hydrolysis reaction of the solution. Electrospinning is performed by choosing a proper feed rate, High voltage value and distance of nozzle to the collector. Process is continued till a thick layer of nanofiber webs are achieved and then calcined at 450 c for 3 hours to attain anatase phase of TiO2. The obtained web has enough strength and flexibility to be lifted gently by clamp. 6 mg of the catalyst was able to degrade 10 ppm Rhodamine B solution throughly in almost 6 hours under UV irradiation. The catalysts preserve its shape after the 6 hours test when it is electrospun by PVAc.. Keywords: electrospinning; TiO2 nanofibers; photocatalytic activity; PVAc 1. Introduction Titania is a wide bandgap semiconductor with many interesting properties, such as transparency to visible light, high refractive index, low absorption coefficient and catalysis[1]. One-dimensional nanostructures of Titania have been a subject of intense research because of their high specific surface area which makes them a good choice to purify waste water[2, 3]. Webs of TiO2 nanofibers have been electrospun in different research works using different auxiliary polymers like Polyvinyl pyrrolidone(PVP)[4-6] and polyvinyl acetate(PVAc)[2, 3, 7]. Ethanol is used as the polymer solvent in the solution. A titanium sol is used in the solution to attain pure TiO2 in the final product after heat treatment of nanofibers. The obtained nanofibers are brittle. Therefore for good ability of the catalyst to degrade the water pollutants to organic materials, a powder of nanofibers are dispersed in waste water using sonication. Thus a centrifuge stage is needed to remove the nanofibers from the water. In this paper we have presented the best ratios of materials in electrospinning process to attain TiO2 nanofibers. These solution ratios will be sufficient for fabricating TiO2 in other structures like yarn which can mentain its structure after heat setting. The purpose of this study is to have a photocatalysis test without a sonication and centrifuge step. The reuseability of the catalyst will be in the long-term application. Photocatalysis tests are performed using Rhodamine B(RhB) as a model pollutant. 2. Materials PVAc (sigma-aldrich) with Mw=100000 is the polymer used in this paper. From different solvents of PVAc ethanol was the best solvent in electrospinning of nanofibers. Glacial Acetic acid (sigma-aldrich) is used to prevent hydrolyzing Titanium sol. Titanium tetra iso propoxide (TTIP 97%, sigma Aldrich) is used as a titanium sol in the solution. 2.1 Method 0.17 gr of PVAc is solved in 1 cc of ethanol and stirred for 10 hours. Then 0.5 cc of acetic acid is added to the solution with stirring for 15 min. Then TTIP is added to the solution and then it is stirred for another 30 hours. The solution becomes milky when it is ready to electrospin. Electrospinning is carried out by setting the distance between the nozzle to collector to 9 cm, feeding rate of 0.2 ml/hr and High voltage of 13 KV.
  • 2. The International Istanbul Textile Congress 2013 May 30th to June 1th 2013, Istanbul, Turkey 2 Electrospun nanofibers need to be annealed for 450 c for 3 hours. During this process, remained polymer and solvents are omitted from the electrospun nanofibers. Furthermore the amorph TiO2 is converted to the anatase crystalline phase of TiO2. The photocatalytic activities of TiO2 nanofibers were investigated by an analysis of the degradation of dyes under UV illumination. 6 mg of pure TiO2 nanofibers were placed in a glass dish. Then dye solution with the concentration of 10 ppm was poured on catalyst. This dish is then settled in an aluminium enclosed cell (17cm×25cm×10 cm). UV irradiation was provided by three 6W light bulb (6W×3) on top of the dish. The changes in the solution colour show the degradation of dye in the water solution. 2.2 Characterization The nanofiber samples were sputter- coated with gold (SC7620, Quorum Technologies) and their morphology was studied with a scanning electron microscope (Philips XL30) at an accelerating voltage of 25 kV. Analysis of the crystalline structures after heat treatment was performed by XRD diffractometer (X'pert Philips) with Cu Kα radiation (λ=0.15406 nm) in 2Ө range from 10˚ to 80˚ by 0.03˚ sec-1 steps. 3. Results SEM image of the fabricated nanofibers before and after heat treatment is shown in figure 1. The diameter of the nanofibers is calculated using image j software. The fibers have an average diameter of 220-280 nm when they are electrospun. The nanofibers diameter is reduced to 170-180 nm after heat treatment in 450 c for 3 hours. Figure 1. electrospun PVAc/TiO2 hybrid nanofiber (left), TiO2 nanofibers after heat treatment at 450 c for 3 hours(right) As it is clear from the XRD pattern in figure 2, the crystalline TiO2 in anatase phase appears by heating at 450 °C for 3 hours. Figure 2. XRD image of electrospun nanofibers Figure 3a shows the initial dye solution on the catalyst sample without UV irradiation. Photocatalytic degradation of organic dye with UV irradiation after 5 hours is indicated in figure 3b. It is clear that most of
  • 3. The International Istanbul Textile Congress 2013 May 30th to June 1th 2013, Istanbul, Turkey 3 the dye has been degraded in the catalyst dish. After 6 hours of UV irradiation it was found that 6 mg of the catalysts is able to disintegrate dye with 10ppm concentration from the water. Figure 3. dye degradation of the photocatalyst after (a)0 hr-start, (b) 5hr, (c) 6hr 4. Conclusion PVAc is used as the auxiliary polymer for electrospinning of pure TiO2 nanofibers. The heat treated fibers were able to be moved in the petri dish. Dye solution has been poured on the catalyst so that powdering the catalyst is not necessary and it eliminates the need for sonication and centrifuge step in dye degradation. This method can be promoted by putting the catalyst in a gradient to the horizon, and recycle dye solution to pass through the catalyst several times. Fabricating the TiO2 structure with sufficient strength makes it possible to use the catalyst in water without dispersing it. References [1] HASHIMOTO, K., H. IRIE, and A. FUJISHIMA, TiO2 Photocatalysis : A Historical Overview and Future Prospects. Japanese Journal of Applied Physics, 2005. 44(12): p. 8269-8285. [2] Doh, S.J., et al., Development of photocatalytic TiO2 nanofibers by electrospinning and its application to degradation of dye pollutants. Journal of Hazardous Materials, 2008. 154: p. 118-127. [3] Hamadanian, M., A. Akbari, and V. Jabbari, Electrospun Titanium Dioxide Nanofibers: Fabrication, Properties and Its Application in Photo-Oxidative Degradation of Methyl Orange (MO). Fibers and Polymers, 2011. 12(7): p. 880-885. [4] Li, H., W. Zhang, and W. Pan, Enhanced Photocatalytic Activity of Electrospun TiO2 Nanofibers with Optimal Anatase/Rutile Ratio. J. Am. Ceram. Soc., 2011: p. 1-4. [5] Li, D. and Y. Xia, Fabrication of Titania Nanofibers by Electrospinning. Nano letters, 2003. 3(4): p. 555-560. [6] Watthanaaruna, J., V. Pavarajarna, and P. Supaphol, Titanium (IV) oxide nanofibers by combined sol–gel and electrospinning techniques: preliminary report on effects of preparation conditions and secondary metal dopant. Science and Technology of Advanced Materials, 2005. 6: p. 240-245. [7] Wu, N., et al., Characterization of PVAc/TiO2 Hybrid Nanofibers: From Fibrous Morphologies to Molecular Structures. Journal ofApplied Polymer Science, 2009. 112: p. 1481-1485.