JP2005185941A - Natural zeolite-titanium dioxide composite particle - Google Patents

Natural zeolite-titanium dioxide composite particle Download PDF

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JP2005185941A
JP2005185941A JP2003429929A JP2003429929A JP2005185941A JP 2005185941 A JP2005185941 A JP 2005185941A JP 2003429929 A JP2003429929 A JP 2003429929A JP 2003429929 A JP2003429929 A JP 2003429929A JP 2005185941 A JP2005185941 A JP 2005185941A
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titanium dioxide
natural zeolite
composite particle
composite particles
composite
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Masaru Otani
賢 尾谷
Hironori Minoshima
裕典 簑嶋
Tomoyuki Uchiyama
智幸 内山
Keiichiro Matsushima
景一郎 松嶋
Isao Sekiguchi
勲 関口
Hiroshi Yamada
浩 山田
Koji Kono
孝治 河野
Tamaki Wada
環 和田
Takayuki Nakajima
孝之 中島
Yasuhiro Matoba
康浩 的場
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Kowa Chemical Industry Co Ltd
Hokkaido Prefecture
Chuo University
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Kowa Chemical Industry Co Ltd
Hokkaido Prefecture
Chuo University
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a composite particle composed of crushed natural zeolite and powder of titanium dioxide combining adsorption characteristics of the zeolite and optical characteristics of the dioxide serving as a semiconductor photocatalyst. <P>SOLUTION: The particle is a composite particle composed of different ingredients and is formed by adding a crushed natural zeolite and powder of titanium dioxide to a binder-containing solution and spraying-drying the resultant slurry. A photocatalyst consisting of the composite particle composed of crushed zeolite and powder of the dioxide and having an adsorbing ability is also provided. The photocatalyst composite particle catalyzes decomposition reaction of an adsorbed organic compound when excited by irradiation with UV rays. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

この発明はバインダーの付着結合効果と共に天然ゼオライト粉砕物と二酸化チタン粉末から形成される複合粒子に関する。この発明はまた、該複合粒子からなる吸着能を有する光触媒に関する。   The present invention relates to composite particles formed from natural zeolite pulverized material and titanium dioxide powder together with the adhesive bonding effect of the binder. The present invention also relates to a photocatalyst having an adsorption ability comprising the composite particles.

天然ゼオライトはアルミノ珪酸塩系の鉱物であり、イオン交換能、吸着能、分子節能、触媒能など各種の優れた機能を持つ物質である。これは天然鉱物であるがゆえに、不純物の除去による純度の向上、他の材料との複合化などによる高付加価値化が望まれている。しかし、従来、天然ゼオライトを、これと他の材料との複合化およびその光触媒機能化を目指してバインダー含有天然ゼオライトスラリーの噴霧乾燥によって造粒した例は、報告されていない。   Natural zeolite is an aluminosilicate mineral and is a substance having various excellent functions such as ion exchange capacity, adsorption capacity, molecular capacity and catalytic capacity. Since this is a natural mineral, it is desired to increase the added value by improving the purity by removing impurities and combining it with other materials. However, there has been no report on an example of granulating natural zeolite by spray drying of a natural zeolite slurry containing a binder with the aim of combining this with other materials and functionalizing the photocatalyst.

なお、この発明に関連した従来技術として、合成ゼオライトによるn−パラフィンの液相吸着が非特許文献1に、スラリーを噴霧乾燥して造粒する方法が非特許文献2にそれぞれ記載されている。
石油学会誌,32,(5),pp.255-261 (1989) Journal of Chemical Engineering of Japan,Vol.34,No.4,PP.472-478 (2001)
As conventional techniques related to the present invention, liquid phase adsorption of n-paraffin by synthetic zeolite is described in Non-Patent Document 1, and a method of granulating a slurry by spray drying is described in Non-Patent Document 2, respectively.
Journal of Petroleum Society, 32, (5), pp.255-261 (1989) Journal of Chemical Engineering of Japan, Vol. 34, No. 4, PP.472-478 (2001)

この発明は、天然ゼオライトの持つ吸着特性と、半導体光触媒である酸化チタンの持つ光学特性に着目し、これらの特性を併せ持つ天然ゼオライト粉砕物と二酸化チタン粉末との複合粒子を提供することを課題とする。   This invention pays attention to the adsorption characteristic which natural zeolite has, and the optical characteristic which the titanium oxide which is a semiconductor photocatalyst has, and it aims at providing the composite particle of the natural zeolite ground material and titanium dioxide powder which have these characteristics together To do.

この発明は、バインダー含有液中に天然ゼオライト粉砕物と二酸化チタン粉末を加えて得られたスラリーを噴霧乾燥により造粒してなる、異成分からなる複合粒子である。   This invention is a composite particle composed of different components obtained by granulating a slurry obtained by adding a pulverized natural zeolite and titanium dioxide powder into a binder-containing liquid by spray drying.

二酸化チタンの含有割合は、天然ゼオライト粉砕物と二酸化チタン粉末の混合物に対して好ましくは10〜70重量%である。   The content of titanium dioxide is preferably 10 to 70% by weight based on the mixture of the natural zeolite pulverized product and titanium dioxide powder.

バインダーの含有割合は、天然ゼオライト粉砕物と二酸化チタン粉末の混合物に対して好ましくは1〜40重量%である。   The content of the binder is preferably 1 to 40% by weight based on the mixture of the natural zeolite pulverized product and the titanium dioxide powder.

好ましい複合粒子は、天然ゼオライト粒子群の表面に二酸化チタン微粒子を固着した組織から構成されてなる凝集構造の形態をなすものである。   A preferable composite particle is in the form of an aggregate structure composed of a structure in which titanium dioxide fine particles are fixed to the surface of a natural zeolite particle group.

天然ゼオライト粉砕物の粒子直径は好ましくは20μm以下である。   The particle diameter of the natural zeolite pulverized product is preferably 20 μm or less.

この発明は、天然ゼオライト粉砕物と二酸化チタン粉末の複合粒子からなる吸着能を有する光触媒を提供する。この光触媒複合粒子は、紫外線の照射により励起されることによって吸着物の有機化合物に対して分解反応を触媒する。   The present invention provides a photocatalyst having an adsorptive capacity composed of composite particles of pulverized natural zeolite and titanium dioxide powder. The photocatalyst composite particles catalyze a decomposition reaction on the organic compound of the adsorbate by being excited by irradiation with ultraviolet rays.

ゼオライトのような多孔性物質はいろいろ存在するが、本発明によれば、ゼオライトは活性炭と比較して極性ガスを吸着しやすいという特徴、さらに天然ゼオライトのもつブロードな細孔分布に由来する吸着速度の速さと吸着物質の選択幅が広いという吸着特性と、半導体光触媒である二酸化チタンの光学特性とを合わせもち、尚且つ、噴霧乾燥造粒による複合粒子のハンドリング特性の改善、吸着と光分解性に優れた天然ゼオライト粉砕物と二酸化チタン粉末による緻密構造の複合粒子を提供することができ、様々な用途への展開が期待される。   Various porous materials such as zeolite exist, but according to the present invention, zeolite is more easily adsorbed with polar gas than activated carbon, and further, the adsorption rate derived from the broad pore distribution of natural zeolite. The combination of the adsorption characteristics of the speed of adsorption and the wide selection of adsorbents and the optical characteristics of titanium dioxide, a semiconductor photocatalyst, improves the handling characteristics of composite particles by spray drying granulation, adsorption and photodegradability It is possible to provide composite particles having a dense structure of natural zeolite pulverized product and titanium dioxide powder, which are expected to be used in various applications.

この発明で用いる天然ゼオライトとしては北海道余市町産に代表されるクリノブチロライトのものが好ましい。これは表1で示すような基礎的な特性を有する。

Figure 2005185941
The natural zeolite used in the present invention is preferably clinoptilolite typified by Yoichi, Hokkaido. This has basic characteristics as shown in Table 1.
Figure 2005185941

図1(a)及び図1(b)は、それぞれ合成ゼオライト及び天然ゼオライト(クリノブチロライト)の細孔分布をFISONS INSTRUMENTS社製ガス吸着式細孔分布測定装置「SORPTMATIC 1990」で測定した結果を示す。ここで示す合成ゼオライトの細孔分布は10〜50nm(1Å=0.1nm)の細孔半径に鋭く集中したミクロ型であり、ほぼ市販品の合成ゼオライトの性状に近い。また天然ゼオライト(余市産)の細孔分布はミクロ型からマクロ型にわたって広い分布を有する細孔半径(10〜600nm)から成り立っている。   Fig. 1 (a) and Fig. 1 (b) show the results of measuring the pore distribution of synthetic zeolite and natural zeolite (clinobyrolite) with a gas adsorption type pore distribution measuring device "SORPTMATIC 1990" manufactured by FISONS INSTRUMENTS, respectively. Indicates. The pore distribution of the synthetic zeolite shown here is a micro type that is sharply concentrated on the pore radius of 10 to 50 nm (1Å = 0.1 nm), and is almost similar to the properties of commercially available synthetic zeolite. Moreover, the pore distribution of natural zeolite (produced by Yoichi) is composed of pore radii (10 to 600 nm) having a wide distribution from the micro type to the macro type.

この発明においては、二酸化チタン粉末は、アナターゼ型、ルチル型、ブルッカイト型、または二酸化チタンへドーピング、色素増感などを行うことにより可視光域の光で励起される可視光応答型光触媒のいずれでもよいが、通常はアナターゼ型が多く用いられる。バインダー含有液は非水溶性の微粒子で、水によく分散するもの(ベントナイト、セメント、消石灰等)、水溶性のもの(デキストリン、アルギン酸塩、水ガラス等)、または反応により第三物質をつくるもの(水ガラスと炭酸、消石灰と糖蜜等)等を含む液、例えば水溶液であってよい。  In the present invention, the titanium dioxide powder is an anatase type, rutile type, brookite type, or any visible light responsive photocatalyst that is excited by light in the visible light region by doping titanium dioxide, dye sensitization, or the like. Usually, anatase type is often used. Binder-containing liquid is water-insoluble fine particles that disperse well in water (bentonite, cement, slaked lime, etc.), water-soluble (dextrin, alginate, water glass, etc.), or those that produce a third substance by reaction It may be a liquid containing water glass and carbonic acid, slaked lime and molasses, etc., for example, an aqueous solution.

バインダーの含有量は、大きくなるに従ってバインダーとしての効果が大きく現れ、かつ複合粒子の強度も増加するが、その一方バインダーが二酸化チタン微粒子を被覆してしまい、光触媒効果を低下させてしまうこととなる。また、バインダー含有液に天然ゼオライト粉砕物と二酸化チタン粉末を加えて得られたスラリーの噴霧乾燥による複合粒子の大きさは、噴霧乾燥の特徴から百数十μm以下であるが、大きい粒子径側に生成された複合粒子ほど、光がその内部中心まで到達しにくくなる。このことから生成複合粒子は、小さい粒子径側に制御し、かつ仕様用途に合わせて適当な材料配合比と共にバインダーの選定とその含有量を決定すればよい。水ガラスを使用した場合には天然ゼオライト粉砕物と二酸化チタン粉末の混合物に対し40重量%以上含有させた場合において光触媒効果がほとんど確認できなくなった。   The binder content increases as the binder content increases, and the strength of the composite particles also increases. On the other hand, the binder coats the titanium dioxide fine particles, thereby reducing the photocatalytic effect. . In addition, the size of the composite particles by spray drying of the slurry obtained by adding natural zeolite pulverized product and titanium dioxide powder to the binder-containing liquid is less than a few tens of μm due to the characteristics of spray drying. The more the composite particles produced in (1), the more difficult it is for light to reach the inner center. From this, the produced composite particles can be controlled on the small particle diameter side, and the binder selection and content can be determined together with an appropriate material blending ratio in accordance with the specification application. When water glass was used, the photocatalytic effect could hardly be confirmed when it was contained in an amount of 40% by weight or more based on the mixture of the pulverized natural zeolite and the titanium dioxide powder.

つぎに、この発明を具体的に説明するために、この発明の実施例およびこれとの比較を示す比較例をいくつか挙げ、さらに得られた各複合粒子の性能試験を示す。   Next, in order to specifically explain the present invention, some examples of the present invention and comparative examples showing comparison with the examples are given, and performance tests of the obtained composite particles are shown.

実施例1〜6
天然ゼオライト粉砕物(北海道余市町産)と、二酸化チタン粉末(アナターゼ型、個数中位直径0.003μm)とを、バインダー含有液としての水ガラス水溶液中で混合し、これに塩酸の添加と共に撹拌調製(pH=8)によりスラリー状とすることにより、噴霧乾燥用の原液試料を調製した。試料の調製条件を表2に示す。得られたスラリーを、スプレードライヤー(大川原化工機社製「L-8型」)を用いて試料供給量4.0×10-4・s-1及びアトマイザー回転数15000rpmの条件で噴霧乾燥により造粒し、複合粒子試料(ZTW-2からZTW−7)を調製した。
Examples 1-6
Natural zeolite ground product (produced in Yoichi-cho, Hokkaido) and titanium dioxide powder (anatase type, number median diameter 0.003μm) are mixed in a water glass aqueous solution as a binder-containing solution, and this is stirred and added with hydrochloric acid. A stock solution sample for spray drying was prepared by slurrying with (pH = 8). Table 2 shows the sample preparation conditions. The obtained slurry is granulated by spray drying using a spray dryer (“L-8 type” manufactured by Okawara Chemical Industries Co., Ltd.) under the conditions of a sample supply rate of 4.0 × 10 −4 · s −1 and an atomizer speed of 15000 rpm. Composite particle samples (ZTW-2 to ZTW-7) were prepared.

比較例1
二酸化チタン粉末及び水ガラスを用いない点を除いて実施例1と同様に操作を行い、天然ゼオライト粉砕物のみからなる造粒物の球状粒子(ZW-1)を調製した。
Comparative Example 1
Except that the titanium dioxide powder and water glass were not used, the same operation as in Example 1 was carried out to prepare granulated spherical particles (ZW-1) consisting only of pulverized natural zeolite.

比較例2,3
実施例1と同様に操作を行い、天然ゼオライト粉砕物と二酸化チタン粉末(TiO2 )の混合物に対してTiO2の重量比で9%及び71.1%とした球状複合粒子(ZTW-l、ZTW-8)を調製した。
Comparative Examples 2 and 3
Spherical composite particles (ZTW-l, ZTW-) having the same TiO 2 weight ratio of 9% and 71.1% with respect to the mixture of pulverized natural zeolite and titanium dioxide powder (TiO 2 ) were performed in the same manner as in Example 1. 8) was prepared.

比較例4
実施例1と同様に操作を行い、天然ゼオライト粉砕物の代わりに合成ゼオライト粉末(和光純薬社製「モレキュラーシーブスlinde 13X」)を使用し、合成ゼオライトとTiO2の混合物に対してTiO2の重量比で50%とした球状複合粒子AZTW-1を調製した。

Figure 2005185941
Comparative Example 4
Treating as in Example 1, using instead synthetic zeolite powder natural zeolite ground material (manufactured by Wako Pure Chemical Industries, Ltd., "molecular sieves linde 13X"), of TiO 2 with respect to the mixture of synthetic zeolite and TiO 2 Spherical composite particles AZTW-1 having a weight ratio of 50% were prepared.
Figure 2005185941

性能試験
実施例及び比較例で得られた複合粒子について、次の方法で性能試験を行った。
Performance test About the composite particle obtained by the Example and the comparative example, the performance test was done with the following method.

a)粒子特性
図2は代表例として複合粒子(ZTW-6)の走査型電子顕微鏡の写真を示す。この粒子は同図中の(a)から球状の複合粒子であることが確認され、また同図中の(b)から、この複合粒子の表面が破砕状ゼオライト結晶粒子の集合状態による大きな細孔構造になっており、微小粒子のTiO2が高分散していることが確認された。
a) Particle characteristics Fig. 2 shows a scanning electron microscope photograph of a composite particle (ZTW-6) as a representative example. This particle is confirmed to be a spherical composite particle from (a) in the figure, and from (b) in the figure, the surface of this composite particle has large pores due to the aggregated state of crushed zeolite crystal particles. The structure was confirmed, and it was confirmed that the fine particles of TiO 2 were highly dispersed.

複合粒子の粒径は、画像処理システム(ニレコ社製LUZEX5000X)により測定し、表3中の個数中位直径で示すように49〜52μmであった。 The particle size of the composite particles was measured by an image processing system (LUZEX5000X manufactured by Nireco Co.), and was 49 to 52 μm as indicated by the number-median diameter in Table 3.

複合粒子の流動性については、パウダーテスター(ホソカワミクロン社製)により測定し、この結果は表3中で安息角と圧縮度で示す。安息角は別に測定した天然ゼオライト粉砕生成物(個数中位直径54μm)の48.7[deg]に比べて27.0〜28.4[deg]のように低い値となり、さらに圧縮度は同じく天然ゼオライト粉砕生成物の39.3重量%に比べて10〜11重量%の低い値を示した。従って、複合粒子群の流動性は非常に良好であった。

Figure 2005185941
The fluidity of the composite particles was measured with a powder tester (manufactured by Hosokawa Micron), and the results are shown in Table 3 as the angle of repose and the degree of compression. The angle of repose is 27.0-28.4 [deg] lower than 48.7 [deg] of the natural zeolite ground product (number median diameter 54 μm) measured separately, and the degree of compression is also the same as that of the natural zeolite ground product. The value was as low as 10-11% by weight compared to 39.3% by weight. Therefore, the fluidity of the composite particle group was very good.
Figure 2005185941

b)複合粒子の吸着・光学特性及び二酸化チタン含有率
恒温振盪槽(温度:25℃)にて濃度0.2[kg・m -3]]のメチレンブルー水溶液に複合粒子50×10- 6 [kg・m-3]]-メチレンブルー水溶液]を加え、吸着平衡に至るまで振盪撹拌を行った後、残存溶液の吸光度を紫外・可視光光度計(島津製作所製、UV-1200)を用いて測定し、平衡濃度を求めた。この結果として図3は平均吸着量q[kg/kg]と平衡濃度C[kg/m3]との関係を示す。この図において、複合粒子中の二酸化チタン粉末の含有率が大きくなるに従って平均吸着量が低下していることがわかる。しかし、複合粒子中の二酸化チタン粉末含有率が67重量%(ZTW-7)においても天然ゼオライト(ZW-1)のもつ平均吸着量の50%以上の平均吸着量を有しており、複合粒子として天然ゼオライトの吸着能力を発揮させるためには、二酸化チタン粉末の含有率はおよそ70重量%以下であることが好ましい。
b) Adsorption and optical properties and titanium dioxide content thermostatic shaking bath of the composite particles (temperature: 25 ° C.) at a concentration 0.2 [kg · m -3]] composite particles in aqueous solution of methylene blue 50 × 10 in - 6 [kg・ M- 3 ]]-Methylene blue aqueous solution] was added, and after stirring and stirring until adsorption equilibrium was reached, the absorbance of the remaining solution was measured using an ultraviolet / visible photometer (manufactured by Shimadzu Corporation, UV-1200). The equilibrium concentration was determined. As a result, FIG. 3 shows the relationship between the average adsorption amount q [kg / kg] and the equilibrium concentration C [kg / m 3 ]. In this figure, it can be seen that the average adsorption amount decreases as the content of the titanium dioxide powder in the composite particles increases. However, even when the content of titanium dioxide powder in the composite particles is 67% by weight (ZTW-7), the composite particles have an average adsorption amount of 50% or more of the average adsorption amount of natural zeolite (ZW-1). In order to exhibit the adsorption ability of natural zeolite, the content of titanium dioxide powder is preferably about 70% by weight or less.

次いで、紫外線照射実験では、各複合粒子試料(ZW-1のみは二酸化チタンを含有せず)とも粒子中に含まれる天然ゼオライト量がいずれも等量0.4×10-3 [kg]になるように複合粒子重量を秤量し、それぞれの複合粒子試料ごとに1.0×10-2 [kg・m-3]のメチレンブルー水溶液50×10-63(50ml)に加え、紫外線照射(8W、波長:356nm、 UVランプ-試料間距離:100mm)及び非照射のもとで残存メチレンブルー水溶液の吸光度測定を行った。
表4は各複合粒子について紫外線の照射時間10000[s]後におけるメチレンブルー残留濃度の測定結果を示す。表中のC0[kg・m-3]は紫外線の非照射(液相吸着のみ)におけるメチレンブルー残留濃度、C1[kg・m-3]は紫外線の照射後のメチレンブルー残留濃度、さらにΔC[kg・m-3]は紫外線のC0とC1の差、すなわち10000[s]経過後のメチレンブルー残留濃度の変化である。

Figure 2005185941
Next, in the ultraviolet irradiation experiment, the amount of natural zeolite contained in each composite particle sample (ZW-1 alone does not contain titanium dioxide) is equal to 0.4 × 10 −3 [kg]. Weigh the composite particles and add 1.0 × 10 -2 [kg · m −3 ] methylene blue aqueous solution 50 × 10 −6 m 3 (50 ml) to each composite particle sample, and then UV irradiation (8 W, wavelength: 356 nm) UV lamp-sample distance: 100 mm) and the absorbance of the remaining aqueous methylene blue solution was measured under non-irradiation.
Table 4 shows the measurement results of the residual concentration of methylene blue after each ultraviolet irradiation time of 10,000 [s] for each composite particle. In the table, C 0 [kg · m −3 ] is the residual concentration of methylene blue in the non-irradiation of ultraviolet rays (liquid phase adsorption only), C 1 [kg · m −3 ] is the residual concentration of methylene blue after the irradiation of ultraviolet rays, and ΔC [ kg · m −3 ] is the difference between UV C 0 and C 1 , that is, the change in the residual concentration of methylene blue after 10000 [s].
Figure 2005185941

なお、図4はメチレンブルー残留濃度の経時変化の代表例として複合粒子(ZTW-3)の紫外線照射とその非照射の場合におけるメチレンブルー残留濃度C1[kg・m-3]と時間t[s]の関係を示しておく。 In addition, FIG. 4 shows the methylene blue residual concentration C 1 [kg · m −3 ] and time t [s] as a representative example of the time-dependent change of the methylene blue residual concentration when the composite particle (ZTW-3) is irradiated with ultraviolet rays and without irradiation. Let's show the relationship.

以上の結果、紫外線照射における各複合粒子(ZWT-1〜7)は、メチレンブルー水溶液残留濃度の減少傾向が認められ、吸着物質(メチレンブルー)が複合粒子の光触媒作用によって分解されていることがわかる。しかし、複合粒子中の二酸化チタン粉末含有率が10重量%以下の複合粒子(ZWT-1)では、メチレンブルー水溶液残留濃度の低下が非常に小さく、二酸化チタンの光触媒効果があまり発揮されていないことが推測される。十分な効果を発揮させるためには二酸化チタンの含有率は10重量%以上が好ましい。   As a result of the above, each composite particle (ZWT-1 to 7) in the ultraviolet irradiation has a tendency of decreasing the residual concentration of the methylene blue aqueous solution, and it can be seen that the adsorbed substance (methylene blue) is decomposed by the photocatalytic action of the composite particle. However, in the composite particles (ZWT-1) having a titanium dioxide powder content of 10% by weight or less in the composite particles, the decrease in the residual concentration of the methylene blue aqueous solution is very small, and the photocatalytic effect of titanium dioxide is not exhibited so much. Guessed. In order to exhibit a sufficient effect, the content of titanium dioxide is preferably 10% by weight or more.

以上のことから天然ゼオライトのもつ吸着特性と、半導体光触媒である二酸化チタンの持つ光学特性とを合わせ持つ複合粒子の二酸化チタン含有率は、所望の用途によって適宜選択すればよいが、10重量%以上70重量%以下が好ましい。   From the above, the titanium dioxide content of the composite particles having both the adsorption characteristics of natural zeolite and the optical characteristics of titanium dioxide, which is a semiconductor photocatalyst, may be appropriately selected depending on the desired application. 70 weight% or less is preferable.

次の実験では、天然ゼオライト粉砕物のみによる造粒粒子 (ZW-1)、複合粒子(ZWT-6)、並びに天然ゼオライトと二酸化チタンの混合物(配合比率はZWT-6と同一)の三つの試料に関して、それぞれの試料について3×10-4kg(0.30g)の一定重量を濃度7.5×10-3 [kg・m-3 ] のメチレンブルー水溶液40×10-63(40ml)に加え、紫外線照射(24時間照射)後に乾燥させてから表面状態の色を観察した。これを図5の写真に示す。この光触媒効果に関する実験において、図5中の左側は、天然ゼオライトのみの造粒粒子(ZW-1)であって、この造粒粒子(ZW-1)に吸着したメチレンブルーが光分解していない状態が観察された。複合粒子ZWT-6の場合には図5中の右に示すように吸着と光分解の繰り返しによってメチレンブルーの色がほとんど消滅した状態が観察された。さらに図5中の中央は天然ゼオライトと二酸化チタンの混合物(非複合粒子)であって、複合粒子(ZWT-6)と同一の配合比にも拘わらず、メチレンブルーの消滅程度が複合粒子(ZWT-6)よりも小さいことが観察された。吸着材(天然ゼオライト粉砕物)と光触媒(二酸化チタン粉末)を単に混合するよりも、複合化を行うことによって光触媒効果がより効率的に発揮されることが推測される。 In the next experiment, three samples of granulated particles (ZW-1), composite particles (ZWT-6), and a mixture of natural zeolite and titanium dioxide (mixing ratio is the same as ZWT-6) using only natural zeolite ground product. For each sample, a constant weight of 3 x 10 -4 kg (0.30 g) is added to 40 x 10 -6 m 3 (40 ml) of methylene blue aqueous solution with a concentration of 7.5 x 10 -3 [kg · m -3 ] and UV After drying (irradiation for 24 hours), the surface state color was observed after drying. This is shown in the photograph of FIG. In the experiment on the photocatalytic effect, the left side in FIG. 5 is a granulated particle (ZW-1) of only natural zeolite, and the methylene blue adsorbed on the granulated particle (ZW-1) is not photolyzed. Was observed. In the case of the composite particle ZWT-6, a state in which the color of methylene blue almost disappeared due to repeated adsorption and photolysis was observed as shown on the right in FIG. Furthermore, the center in FIG. 5 is a mixture of natural zeolite and titanium dioxide (non-composite particles), and the degree of disappearance of methylene blue is the composite particles (ZWT-) despite the same blending ratio as the composite particles (ZWT-6). It was observed to be smaller than 6). It is presumed that the photocatalytic effect is more efficiently exhibited by performing the composite than simply mixing the adsorbent (natural zeolite pulverized product) and the photocatalyst (titanium dioxide powder).

c)複合粒子の吸着率とその経時変化
本実験ではバッフル付撹拌槽にて濃度0.36[kg・m-3]のメチレンブルー水溶液に複合粒子8.0×10-3[kg]を加え、攪拌機の回転数700rpmで3時間の回分吸着を行い、槽内の採取液の吸光度を紫外・可視光光度計(島津製作所製、UV-1200)によって測定し、この値から槽内液中のメチレンブルー濃度を求めた。こうして得られた値を複合粒子に吸着された吸着量qに換算し、さらに平衡吸着量q0に対する吸着量qの比、すなわち吸着率y(=q/q0)は時間t[s]との関係としてプロットしたのが図6である。この図において、吸着率yは複合粒子の各試料(ZW-1、ZTW3,7,5)のいずれにおいても急速に増加し、その後では徐々に吸着される状態を示している。これは図1(b)に天然ゼオライト(余市産)の細孔分布で示すように細孔径の大きい部分があるために、複合粒子内の拡散抵抗が少なく、ほとんど瞬間的に吸着される利点がある。さらに緩慢な吸着過程では小さな細孔径に依存して拡散抵抗の影響が表れている部分と推察される。
c) Adsorption rate of composite particles and its change over time In this experiment, 8.0 × 10 -3 [kg] of composite particles was added to a methylene blue aqueous solution with a concentration of 0.36 [kg · m -3 ] in a baffled stirring tank, and the rotation speed of the stirrer Absorption was performed at 700 rpm for 3 hours, and the absorbance of the collected liquid in the tank was measured with an ultraviolet / visible photometer (manufactured by Shimadzu Corporation, UV-1200), and the methylene blue concentration in the liquid in the tank was determined from this value. . The value thus obtained is converted into an adsorption amount q adsorbed on the composite particles, and the ratio of the adsorption amount q to the equilibrium adsorption amount q 0 , that is, the adsorption rate y (= q / q 0 ) is expressed as time t [s]. FIG. 6 is a plot of the relationship. In this figure, the adsorption rate y rapidly increases in each of the composite particle samples (ZW-1, ZTW3, 7, 5), and then gradually adsorbs. As shown in the pore distribution of natural zeolite (produced by Yoichi) in Fig. 1 (b), there is a part with a large pore diameter, so there is little diffusion resistance in the composite particles, and the advantage is that it is adsorbed almost instantaneously. is there. Furthermore, in the slow adsorption process, it is inferred that the influence of diffusion resistance appears depending on the small pore diameter.

これに対して合成ゼオライトを用いた複合粒子(AZW-1)は、天然ゼオライトを用いた複合粒子のような初期の急速な吸着がみられず、緩慢な吸着過程をもつことがわかる。これは、図1(a)合成ゼオライトの細孔分布で示すように、細孔径が非常に小さく、シャープな細孔分布をもつことから複合粒子内の拡散抵抗が大きいことによるものと推察される。また、水ガラスをバインダーとした天然ゼオライト(余市産)のみによる複合粒子(ZW-1)では、吸着率yが最も高くなる。これに対して複合粒子中に二酸化チタン粉末を含む場合(ZTW3,5,7)では、二酸化チタン量の増加と共に吸着率がやや低下するが、いずれも吸着率が0.85以上となる良好な傾向を示す。   In contrast, composite particles using synthetic zeolite (AZW-1) do not show rapid initial adsorption as in composite particles using natural zeolite, and have a slow adsorption process. This is presumed to be due to the large diffusion resistance in the composite particles because the pore diameter is very small and the pore distribution is sharp, as shown in FIG. 1 (a). . In addition, the adsorption rate y is the highest in the composite particles (ZW-1) made of only natural zeolite (Yoichi) with water glass as a binder. On the other hand, when the composite particles contain titanium dioxide powder (ZTW3, 5, 7), the adsorption rate decreases slightly as the amount of titanium dioxide increases, but in both cases, the adsorption rate tends to be 0.85 or higher. Show.

図1(a)は、合成ゼオライトの細孔分布をFISONS INSTRUMENTS社製ガス吸着式細孔分布測定装置「SORPTMATIC 1990」で測定した結果を示すグラフである。FIG. 1 (a) is a graph showing the results of measuring the pore distribution of a synthetic zeolite using a gas adsorption type pore distribution measuring device “SORPTMATIC 1990” manufactured by FISONS INSTRUMENTS. 図1(b)は、天然ゼオライト(クリノブチロライト)の細孔分布をFISONS INSTRUMENTS社製ガス吸着式細孔分布測定装置「SORPTMATIC 1990」で測定した結果を示すグラフである。FIG. 1 (b) is a graph showing the results of measuring the pore distribution of natural zeolite (clinobyrolite) with a gas adsorption pore distribution measuring device “SORPTMATIC 1990” manufactured by FISONS INSTRUMENTS. 図2(a)は、複合粒子(ZTW-6)の走査型電子顕微鏡の写真である。FIG. 2 (a) is a scanning electron microscope photograph of the composite particle (ZTW-6). 図2(b)は、この複合粒子の表面の走査型電子顕微鏡の写真である。FIG. 2 (b) is a scanning electron microscope photograph of the surface of the composite particle. 図3は、平均吸着量q[kg/kg]と平衡濃度C[kg/m3]との関係を示すグラフである。FIG. 3 is a graph showing the relationship between the average adsorption amount q [kg / kg] and the equilibrium concentration C [kg / m 3 ]. 図4は、メチレンブルー残留濃度の経時変化の代表例として複合粒子(ZTW-3)の紫外線照射とその非照射の場合におけるメチレンブルー残留濃度C1[kg・m-3]と時間t[s]の関係を示すグラフである。Fig. 4 shows the methylene blue residual concentration C 1 [kg · m -3 ] and time t [s] as a representative example of the time-dependent change in the methylene blue residual concentration when the composite particle (ZTW-3) is irradiated with ultraviolet light and without irradiation. It is a graph which shows a relationship. 図5は、天然ゼオライト粉砕物のみによる造粒粒子 (ZW-1)、複合粒子(ZWT-6)、並びに天然ゼオライトと二酸化チタンの混合物(配合比率はZWT-6と同一)の三つの試料に関して、各試料をメチレンブルー水溶液に加え、紫外線照射後に乾燥させた表面状態を示す写真である。Figure 5 shows three samples of granulated particles (ZW-1), composite particles (ZWT-6), and a mixture of natural zeolite and titanium dioxide (mixing ratio is the same as ZWT-6). FIG. 4 is a photograph showing a surface state in which each sample was added to a methylene blue aqueous solution and dried after ultraviolet irradiation. 図6は吸着率y(=q/q0)と時間t[s]との関係を示すグラフである。FIG. 6 is a graph showing the relationship between the adsorption rate y (= q / q 0 ) and the time t [s].

Claims (6)

バインダー含有液中に天然ゼオライト粉砕物と二酸化チタン粉末を加えて得られたスラリーを噴霧乾燥により造粒してなる、異成分からなる複合粒子。 Composite particles composed of different components obtained by granulating a slurry obtained by adding a natural zeolite pulverized product and titanium dioxide powder into a binder-containing liquid by spray drying. 二酸化チタンが天然ゼオライト粉砕物と二酸化チタン粉末の混合物に対して10〜70重量%の割合で含まれている請求項1記載の複合粒子。 2. The composite particles according to claim 1, wherein titanium dioxide is contained in a proportion of 10 to 70% by weight based on the mixture of the natural zeolite pulverized product and the titanium dioxide powder. バインダーが天然ゼオライト粉砕物と二酸化チタン粉末の混合物に対して1〜40重量%の割合で含まれている請求項1記載の複合粒子。 The composite particle according to claim 1, wherein the binder is contained in an amount of 1 to 40% by weight based on the mixture of the natural zeolite pulverized product and the titanium dioxide powder. 天然ゼオライト粒子群の表面に二酸化チタン微粒子を固着した組織から構成されてなる凝集構造の形態をなす請求項1記載の複合粒子。 The composite particle according to claim 1, wherein the composite particle is in the form of an agglomerated structure composed of a structure in which titanium dioxide fine particles are fixed on the surface of the natural zeolite particle group. 天然ゼオライト粉砕物の粒子直径が20μm以下である請求項1記載の複合粒子。 The composite particle according to claim 1, wherein the natural zeolite pulverized product has a particle diameter of 20 µm or less. 請求項1〜5のいずれかに記載の複合粒子からなる、吸着能を有する光触媒。
A photocatalyst having an adsorption capacity, comprising the composite particles according to claim 1.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012515644A (en) * 2009-01-23 2012-07-12 エフェエメセ フォレト,ソシエダ アノニマ Photocatalytic mixture for the decomposition of nitrogen oxides
CN103165876A (en) * 2011-12-15 2013-06-19 新奥科技发展有限公司 A preparation method and applications of a lithium battery material with high rate performance

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012515644A (en) * 2009-01-23 2012-07-12 エフェエメセ フォレト,ソシエダ アノニマ Photocatalytic mixture for the decomposition of nitrogen oxides
CN103165876A (en) * 2011-12-15 2013-06-19 新奥科技发展有限公司 A preparation method and applications of a lithium battery material with high rate performance
CN103165876B (en) * 2011-12-15 2016-08-31 新奥科技发展有限公司 A kind of preparation method and its usage of the lithium battery material possessing high rate capability

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