Wave-guide type photoreactor for water purification

Nobuaki Negishi; Feng He; Sadao Matsuzawa; Koji Takeuchi; Kayo Ohno

doi:10.1016/j.crci.2005.08.001

Account / Revue

Wave-guide type photoreactor for water purification

Nobuaki Negishi ¹ ; Feng He ¹; Sadao Matsuzawa ¹; Koji Takeuchi ¹; Kayo Ohno ¹

¹ National Institute of Advanced Industrial Science and Technology (AIST), AIST-West 16-1, Onogawa, Tsukuba 305-8569, Japan

Comptes Rendus. Chimie, Volume 9 (2006) no. 5-6, pp. 822-828.

Abstracts

English
French

A wave-guide type photocatalytic rod that is consisting of a glass tube with transparent TiO₂ (outside) and an optical wave-guide rod (inside) was designed and examined its performance. A model of polluted water, which contains 100 ppm of toluene or phenol, was taken in a 500 ml of beaker and the performance of this unit was evaluated by the removal rate of pollutants in water under photo-irradiation. Acrylic rod with 6-mm diameter was used as the wave-guide of light. One end of acrylic rod 50 mm had a frosted part or a screw thread for increasing seep out of the light. For the glass tube with transparent TiO₂, four kinds with different film thickness were prepared by the dip-coating method. The wave-guide type photocatalytic rods effectively eliminated toluene and phenol and the total amount of intermediates formation was low. .

Un barreau photocatalytique de type guide d'onde consistant en un tube de verre, recouvert à l'extérieur de TiO₂ transparent et contenant à l'intérieur un barreau guide d'onde optique, a été conçu et ses performances étudiées. Une eau polluée modèle contenant 100 ppm de toluène ou de phénol dans un bécher de 500 ml a été utilisée. La performance du photoréacteur a été évaluée en étudiant la vitesse d'élimination des polluants dans l'eau sous photo-irradiation. Un barreau acrylique de 6 mm de diamètre et de 50 mm de longueur a été utilisé comme guide d'onde de la lumière. Une de ses extrémités a été dépolie ou comporte un filet de vis dans le but d'augmenter la diffusion de la lumière. Le tube de verre a été recouvert de couches de TiO₂ de quatre épaisseurs différentes, préparées par la méthode dite de dip-coating. Les barreaux photocatalytiques de type guide d'onde permettent d'éliminer efficacement le toluène et le phénol avec une quantité totale d'espèces intermédiaires faible. .

Metadata

Received: 2004-09-20
Accepted: 2005-04-26
Published online: 2005-09-19

DOI: 10.1016/j.crci.2005.08.001

Keywords: TiO₂, Photocatalyst, Wave-guide, Aqueous phase, Toluene, Phenol
Keywords: TiO₂, Photocatalyse, Guide d'onde, Phase aqueuse, Toluène, Phénol

Author's affiliations:

Nobuaki Negishi ¹; Feng He ¹; Sadao Matsuzawa ¹; Koji Takeuchi ¹; Kayo Ohno ¹

¹ National Institute of Advanced Industrial Science and Technology (AIST), AIST-West 16-1, Onogawa, Tsukuba 305-8569, Japan

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Nobuaki Negishi; Feng He; Sadao Matsuzawa; Koji Takeuchi; Kayo Ohno. Wave-guide type photoreactor for water purification. Comptes Rendus. Chimie, Volume 9 (2006) no. 5-6, pp. 822-828. doi : 10.1016/j.crci.2005.08.001. https://comptes-rendus.academie-sciences.fr/chimie/articles/10.1016/j.crci.2005.08.001/

Version originale du texte intégral

1 Introduction

Many types of photocatalytic reactors have been proposed for water purification. However, most of reactors use UV lamp that consume an electric power. Activation of photocatalyst by sunlight can decrease the cost for the system. Although some of photocatalytic reactor using sunlight for activation of photocatalyst has been developed, they also require the electricity for circulation of water by pump and so on [1]. The purpose of this research is a development of drinking water purification system using less electricity. This system basically aims at the utilization in isolated islands, mountain huts, and inconvenient places in developing countries. Especially, it is expected that this system will be helpful in developing countries located in tropical or sub-tropical area since enough sunlight can be obtained. Using this water purification system, a lot of people can get purified drinking water and hence can prevent suffering from diseases and improve their health.

So far, using optical fiber coated with TiO₂ has carried out a number of researches on water purification by using optical fiber coated with TiO₂. Two types of optical fiber were used as a substrate for TiO₂ coating. One is quartz fiber, and the other is the polymer optical fiber [2]. The quartz fiber is very stable and the transparency of UV light is high, however, it has a costly problem. Typical polymer optical fiber is made from polymetylmethacrylate (PMMA) resin. This is not so expensive compared with quartz fiber [3], however, this organic fiber is not stable against photocatalytic oxidation.

In this research, we used optical wave-guide rod instead of optical fiber to avoid for mentioned costly and instability problems for optical fibers [5]. Transparent TiO₂ thin film was coated outside of Pyrex glass tube, and the optical wave-guide rod made from PMMA was inserted into this photocatalytic tube. Pollutants are oxidized at the interface between photocatalytic surface and aqueous phase by UV light irradiation of photocatalytic layer from the backside. Here, we report some results about the removal rate of water soluble VOC by the reactor using wave-guide type photocatalytic rods. Final destination of this research is not only removal of organic water pollutant but also sterilization of bacteria in drinking water.

2 Experimental

2.1 Preparation of wave-guide type photocatalytic rod with TiO₂

A glass tube with transparent TiO₂ was prepared by dip-coating method [4]. Tetraisopropyl orthotitanate (TPOT), α-terpineol (TPO), 2-propanol (PrOH), diethyleneglycol monoethyl ether ((ethoxyethoxy)ethanol, EEE) were used to make a solution for dip-coating. EEE was used as ligand for TPOT. TPOT (100 ml), TPO (350 ml), PrOH (250 ml), and EEE (100 ml) were well mixed using a magnetic stirrer before use.

A Pyrex glass tube (external diameter = 9.5 mmϕ, internal diameter = 6.5 mmϕ, length = 150 mm) was dip-coated as follows. Withdrawing speed was 1.5 mm/s, and dip-coating process was carried out under room temperature and ambient air. After that, this glass tube was heated at 450 °C for 1 h to form anatase TiO₂ on the surface. To examine the effect of TiO₂ film thickness, four kinds of glass tube were prepared with different coating times, 3, 6, 9, and 12. Twelve times coating means repeating 12 times, dip-coating and calcination process. TiO₂ film thickness on the glass tube was estimated from field emission scanning electron microscope (FE-SEM) images taken using Hitachi S-4700.

We used transparent acrylic acid resin rod (diameter = 6 mm, length = 150 mm) as a wave-guide for the incident light. Two types of acrylic wave-guide rods were prepared for the purpose of increasing seep out of the light. One of the wave-guide rod had 50 mm of frosted part at the edge, and the other had a screw-cut by stump out using a die.

The wave-guide type photocatalytic rod was prepared by inserting the above wave-guide rod into the photocatalytic tube coated with TiO₂. Sixteen photocatalytic rods were set at vertical position on a Teflon block plinth (50 × 50 × 10 mm) and a photocatalytic unit was constructed. The image of the unit is shown in Fig. 1.

Fig. 1
Image of photocatalytic reactor using wave-guide rods. (1): photocatalytic rod, (2): 500 ml beaker, (3): polluted water, (4): Teflon plinth, (5): Teflon cap.

2.2 Measurement of UV light intensity from wave-guide type photocatalytic rod

The efficiency of water purification depends on UV energy used for oxidation reaction. UV light transmitted inside of the wave-guide mainly seeps out from the frosted or screw-cut section and irradiates the TiO₂ layer from the backside. To obtain an information about suitable TiO₂ film thickness, we measured the intensity of UV light transmitted from the side of each wave-guide inserted photocatalytic rod in the atmosphere. The measurement of the UV intensity emitted from wave-guide type photocatalytic rod was carried out using Fuji Xerox UV Caremate Pro.

2.3 Photocatalytic reactions

The unit of wave-guide type photocatalytic rods prepared in Section 1 was set on a 500 ml glass beaker and used for photocatalytic decomposition of pollutants in a model of polluted solution (500 ml) in a beaker. Toluene and phenol were added as contaminants for a model solution, and the initial concentration was kept at 100 ppm. Top of beaker was sealed with Teflon plate to avoid direct irradiation of water by the UV light source. Irradiation of light was carried out using high-pressure mercury lamp (500 W). The experimental apparatus used in this research is shown in Fig. 2.

Fig. 2
Experimental apparatus for photocatalytic reaction.

Concentration of contaminants and intermediates formed by oxidation reactions was analyzed using HPLC equipped with Shimadzu LC10AC gradient system and GC/MS (Shimadzu GCMS-QP2010).

3 Results and discussion

The method of TiO₂ coating was already reported [4]. For the TiO₂ coated glass tubes, optical measurement of film thickness was difficult because the shape of TiO₂ layer was cylindrical. Therefore, film thickness was estimated by observation of cross section of the glass tube by using FE-SEM. Fig. 3 shows the SEM image of the cross section of the TiO₂ coated photocatalytic rods. As shown in Fig. 3, the thickness of TiO₂ layer linearly increased in proportion to the number of dip-coating. Estimated film thickness of the TiO₂ layer with 3, 6, 9, and 12 time coating were around 0.25, 0.50, 0.75, and 1.00 μm, respectively.

Fig. 3
FE-SEM image of the cross section of a glass tube with TiO₂ coating.
The thickness of TiO₂ layer linearly increases with increasing dip-coating times.

Fig. 4 shows the intensity of UV light seeped out from the photocatalytic rod. 10 cm on a glass tube was coated by TiO₂ thin film. As shown in Fig. 4, seeping out of light from the top 5 cm of the photocatalytic rod is very weak because introduced light is totally reflected at the wall of the wave guide. Introduced UV light into wave-guide rod is seeped out from the bottom 5 cm of photocatalytic rod. Furthermore, UV intensity depends on a difference process of seep-out region between frosted and screw-cut, and film thickness of TiO₂. Maximum UV emission intensity from screw-cut wave-guide inserted photocatalytic rod was around five times of frosted one. Emission from seep out area is depend on a roughness of wave-guide surface. This result shows that an important factor for this system is how to seep out the introduced light to wave-guide rod. Seeping out UV intensity from wave-guide inserted photocatalytic rod decreased with the increase of film thickness as shown in Fig. 4. This result means that absorbance of UV light by TiO₂ layer increases with increasing TiO₂ film thickness.

Fig. 4
Dependence of coating times on UV intensity seeped out from the photocatalytic rod. Left side shows the light intensity from frosted wave-guide inserted photocatalytic tube. Right side shows the light intensity from screw-cut wave guide inserted photocatalytic tube. (1) Shows the image of the frosted wave-guide inserted photocatalytic tube. (1′) Shows the image of the screw-cut wave-guide inserted photocatalytic tube. (2) Shows the seep-out region of UV light from frosted or screw-cut processed on wave-guide rod. (3) Shows the frosted wave-guide rod. (3′) Shows the screw-cut wave-guide rod. (4) Shows the photocatalytic tube.

Fig. 5 shows a relationship between TiO₂ film thickness and penetration of UV light into TiO₂ layer. In this experiment, UV irradiation of TiO₂ photocatalyst is backside direction of coating. Therefore, TiO₂ film thickness is also important factor for reveal of photocatalytic activity. When TiO₂ film thickness is too thin (case (1)), photocatalytic activity is low because absolute amount of photocatalyst usable for photodegradation is small. Similarly, photocatalytic activity may decrease when TiO₂ film thickness is too thick (case (3)). Inside of TiO₂ layer absorbs UV irradiation, and the UV light approached to the photocatalytic area in TiO₂ layer must be decreased, as a result, photocatalytic activity is decreased. At the case (2), excitation light is strong at the photoreaction area. In addition, the amount of photocatalyst is optimum. Therefore, it is expected that photocatalytic activity is high on the case (2).

Fig. 5
Relationship between TiO₂ film thickness and the light penetration into TiO₂ layer from backside. (1) Too thin TiO₂ layer, (2) optimum TiO₂ layer, (3) too thick TiO₂ layer. TiO₂ layer has a porous structure, and reactants penetrate and disperse to inside of the TiO₂ layer.

Fig. 6 shows the result of photocatalytic degradation of 100 ppm toluene in aqueous phase using wave-guide type (with screw-cut rod) photoreactor. Toluene easily evaporates from aqueous phase, therefore, the changes in toluene concentration by evaporation was obtained and compensated for the true amount of degraded toluene by photocatalyst. CO₂ and H₂O have been reported as the final products of the photocatalytic degradation of toluene [5]. In case of gas phase reaction, benzyl alcohol and benzaldehyde were observed as adsorbed intermediate species on a surface of photocatalyst [5]. Although these two intermediate species are soluble in water, we could not detect them in aqueous phase. On the other hand, we found small amount of p-cresol in aqueous phase. The mechanism for following photodegradation of toluene has been proposed (Schema 1).

Fig. 6
Photocatalytic degradation of toluene (100 ppm). The reaction rate depend on a thickness of the TiO₂ layer.

Schema 1
Proposed degradation pathways of toluene. (1): toluene, (2): benzyl alcohol, (3): benzaldehyde, (4):p-cresol.

OH radical plays an important role for photo-oxidation of toluene and further reaction of intermediates. Many researchers reported that benzyl alcohol (2) and benzaldehyde (3) were formed with photocatalytic oxidation of toluene in gas phase [5]. On the other hand, Marci et al. reported that p-cresol (4) was found in aqueous phase [6]. They supposed that high concentration of water would favor the attack of OH radical to the 4-position of toluene molecule. This result indicates that addition reaction of hydroxyl group to benzene ring easily progress compared with oxidation of methyl group under water rich condition. Therefore, benzaldehyde and benzyl alcohol were scarcely observed in aqueous phase in our study.

As shown in Fig. 6, 0.5 μm thick photocatalytic rod gives the highest efficiency. Namely, 0.5 μm of TiO₂ film thickness is suitable for the utilization of wave-guide type photocatalytic rod. This result is agree with forecast in Fig. 5. Film thickness of 0.5 μm corresponds to the case (2) in Fig. 5, which gives optimum penetration of light for photodegradation using the wave-guide type photocatalytic rods.

Phenol is well known environmental contaminant, and it is contained in the waste water from industries. Photodegradation of phenol in aqueous phase has been reported by many researchers. The possible pathway for the photodecomposition of phenol has been reported as follows: (Schema 2).

Schema 2
Proposed degradation pathways of phenol. (5): phenol, (6): catecol, (7): resorcinol, (8): hydroquinone, (9): p-benzoquinone, (10): pyrogallol, (11): phloroglucinol dihydrate, (12): phloroglucinol.

In the case of this photoreactor system, the concentration of phenol did not change with increasing time without UV irradiation.

Fig. 7 shows the result of photodegradation of phenol using the wave-guide type rods. In this experiment, we tested both frosted and screw-cut wave-guide rods. As shown in Fig. 7, concentration of phenol in water decreased with increasing UV irradiation time. The degradation rate depends on the shape of wave-guide and the thickness of TiO₂ layer. Any big difference in the degradation rates was observed between frosted and screw-cut wave-guide made with 0.75 μm TiO₂ coatings. While degradation rate for screw-cut wave-guide was higher than that of frosted one in case 0.5 and 1.0 μm coated rods were used. Screw-cut wave-guide may allow higher transmittance of light and gives similar penetration of light to the case (2) in Fig. 5. More experiments are needed to reveal why 0.75 μm TiO₂ coating gave the best result in case of phenol.

Fig. 7
Photocatalytic degradation of phenol (100 ppm) using photocatalytic rods with different thickness of TiO₂ layer (0.5, 0.75, 1.0 μm) and different kind of wave-guide rods (screw-cut: S, frosted: F).

In our experiment, we detected few ppm level of some intermediate species formed by photodecomposition of phenol [7]. Judging from the result of HPLC analysis, main products were hydroquinone (8) in Schema 2. In addition, trace level of catecol (6), resorcinol (7), and p-benzoquinone (9) was observed by GC/MS analysis. Trihydroxybenzene isomers (10) and (11) were also observed under trace level. However, phloroglucinol (12) was not observed in any analysis method. It is considered that compound (12) is unstable in an aqueous phase. Detection of these trihydroxybenzenes formed in the aqueous system was very difficult since the concentration of dihydroxybenzenes derived from phenol was also very low.

We conclude that total amount of intermediates can be decreased by use of the wave-guide type photocatalytic rods reported here. Photocatalyst on the glass tube seems to depress the dispersion of intermediates to the aqueous phase. Our result shows that the photoreactor using wave-guide rod inserted photocatalytic tube is more suitable than conventional ones for the water purification. We will continue further experiments for practical application of this system with solar light. Measurement of sterilization effect will be also conducted.

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