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JP7499640B2 - Method for treating waste gas containing hydrophobic silica - Google Patents
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JP7499640B2 - Method for treating waste gas containing hydrophobic silica - Google Patents

Method for treating waste gas containing hydrophobic silica Download PDF

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JP7499640B2
JP7499640B2 JP2020137804A JP2020137804A JP7499640B2 JP 7499640 B2 JP7499640 B2 JP 7499640B2 JP 2020137804 A JP2020137804 A JP 2020137804A JP 2020137804 A JP2020137804 A JP 2020137804A JP 7499640 B2 JP7499640 B2 JP 7499640B2
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健治 島岡
務 池田
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Tokuyama Corp
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Description

本発明は疎水性シリカを含む廃ガスの処理方法に関する。詳しくは疎水性シリカを含む廃ガスをバーナーで燃焼処理後、水と接触させることで前記廃ガスを簡便に処理する方法を提供するものである。 The present invention relates to a method for treating waste gas containing hydrophobic silica. More specifically, the present invention provides a method for easily treating waste gas containing hydrophobic silica by burning the waste gas with a burner and then contacting the waste gas with water.

乾式シリカは一般的に樹脂等の増粘・揺変効果や補強効果などの付与を目的に、添加剤として使用されている。これらの所望の応用特性を得るために、使用する樹脂等の種類により、親水性シリカあるいは親水性シリカの表面を疎水化処理した疎水性シリカが適宜、選択される。 Dry silica is generally used as an additive to impart thickening and thixotropy effects and reinforcing effects to resins, etc. In order to obtain these desired application properties, hydrophilic silica or hydrophobic silica with the surface of hydrophilic silica hydrophobized is appropriately selected depending on the type of resin, etc. used.

疎水性シリカは一般に親水性シリカの表面をヘキサメチルジシラザンや環状ジメチルシロキサンなどの有機ケイ素化合物で処理することで、疎水性が付与される。(特許文献1、2等参照)
親水性シリカの表面処理工程では、表面処理のため導入したガスを系外へ排出する必要がある。その際、排出するガスに疎水性シリカが同伴するのが一般的であるため、発生する疎水性シリカを含む廃ガスを処理する工程が必要となる。特に粒径やかさ密度が小さく、ガスに同伴しやすいフュームドシリカの表面処理においては顕著である。
Hydrophobicity is generally imparted to hydrophilic silica by treating the surface of the hydrophilic silica with an organosilicon compound such as hexamethyldisilazane or cyclic dimethylsiloxane (see Patent Documents 1 and 2, etc.).
In the surface treatment process of hydrophilic silica, it is necessary to discharge the gas introduced for the surface treatment outside the system. In this case, hydrophobic silica is generally entrained in the gas discharged, so a process for treating the waste gas containing hydrophobic silica that is generated is required. This is particularly noticeable in the surface treatment of fumed silica, which has a small particle size and bulk density and is easily entrained in gas.

シリカ等の微粒子を含む廃ガスの処理方法としては、水と接触させて含まれる微粒子を水へ懸濁させて除去するなどの方法が考えられるが、疎水性シリカの場合、本質的に水との馴染みが悪いため懸濁させることが困難であるといった問題がある。 One possible method for treating waste gas containing fine particles such as silica is to bring the gas into contact with water to remove the fine particles by suspending them in the water. However, in the case of hydrophobic silica, the problem is that it is difficult to suspend the silica because it is inherently poorly compatible with water.

廃ガスに含まれる微粒子が疎水性シリカである場合には、該ガスを接触させる液体を、疎水性の微粒子が懸濁しやすい有機溶媒として処理する等の方法があるが、使用する有機溶媒の費用や有機溶媒廃液の処理費用が発生するため、疎水性シリカを大量に処理する場合、経済的な面で実現性が低いものである。 When the fine particles contained in the waste gas are hydrophobic silica, one method is to treat the liquid with which the gas comes into contact with an organic solvent in which hydrophobic fine particles are easily suspended. However, this is not economically viable when treating large amounts of hydrophobic silica, as it requires costs for the organic solvent used and for treating the organic solvent waste liquid.

特開平8-259216号公報Japanese Patent Application Laid-Open No. 8-259216 特開2004-352606号公報JP 2004-352606 A

従って、本発明の目的は、疎水性シリカを含む廃ガスを簡便に処理可能な方法について提供するものである。 Therefore, the object of the present invention is to provide a method for easily treating waste gas containing hydrophobic silica.

本発明者は疎水性シリカを含む廃ガスを効率的に処理可能な方法を開発すべく鋭意検討を重ねた。その結果、火炎を形成したバーナーで疎水性シリカを燃焼処理することにより、シリカに疎水性を与えている有機物が燃焼除去され、よってシリカが親水化することで、水への懸濁処理が可能となることを見出し、本発明を完成するに至った。 The inventors conducted extensive research to develop a method for efficiently treating waste gases containing hydrophobic silica. As a result, they discovered that by burning hydrophobic silica with a burner that creates a flame, the organic matter that gives the silica its hydrophobicity is burned and removed, and the silica becomes hydrophilic, making it possible to suspend it in water, which led to the completion of the present invention.

即ち、本発明は、疎水性シリカを含む廃ガスの処理方法であって、当該廃ガスを、バーナーとバーナー下方に設けられた燃焼室を有する燃焼炉で燃焼処理した後、水と接触させる工程を含み、前記燃焼室中に旋回流を生じさせた状態で燃焼処理を行うことを特徴とする前記廃ガスの処理方法である。
That is, the present invention is a method for treating a waste gas containing hydrophobic silica, which comprises a step of combusting the waste gas in a combustion furnace having a burner and a combustion chamber provided below the burner, and then contacting the waste gas with water , characterized in that the combustion treatment is carried out in a state where a swirling flow is generated in the combustion chamber .

本発明の廃ガス処理方法によれば、従来法では処理の困難な疎水性シリカを含んだ廃ガスを、有機溶媒等を使用することなく効率的に処理することが可能となり、廃棄物の処理方法として極めて有用である。 The waste gas treatment method of the present invention makes it possible to efficiently treat waste gas containing hydrophobic silica, which is difficult to treat using conventional methods, without using organic solvents, etc., making it extremely useful as a waste treatment method.

廃ガスには有機ケイ素化合物を含んでいてもよく、その場合、含まれた有機ケイ素化合物は燃焼処理により、親水性シリカとして処理することが可能である。 The waste gas may contain organosilicon compounds, in which case the organosilicon compounds can be treated to produce hydrophilic silica by combustion.

本発明の廃ガスの処理方法で用いられる燃焼炉の一様態を示す横断面模式図。1 is a schematic cross-sectional view showing one embodiment of a combustion furnace used in the waste gas treatment method of the present invention. 本発明における燃焼室の旋回エアー投入方法の一様態を示す上面模式図。FIG. 2 is a schematic top view showing one embodiment of a method for injecting swirling air into a combustion chamber in the present invention.

本発明において、処理の対象となる疎水性シリカを含む廃ガスの発生要因は特に限定されるものではないが、代表的な発生要因の例を挙げると以下のようなものがある。 In the present invention, the cause of the generation of waste gas containing hydrophobic silica to be treated is not particularly limited, but typical examples of the generation causes are as follows:

疎水性シリカを原料として使用するプロセスから排出されるガス、具体的には排煙脱硫装置にて脱硫成分の固結防止剤として疎水性シリカを用いている場合に当該排煙脱硫装置から排出されるガス、シリコーン材料あるいはその他の樹脂組成物の製造時に、フィラーとして疎水性シリカを配合・混練する工程において排出されるガス(より具体的には、例えば真空処理における吸気ガス)などが挙げられる。 Gases discharged from processes that use hydrophobic silica as a raw material, specifically gases discharged from flue gas desulfurization equipment when hydrophobic silica is used as an anti-caking agent for desulfurization components in the equipment, and gases discharged in the process of compounding and kneading hydrophobic silica as a filler during the manufacture of silicone materials or other resin compositions (more specifically, intake gas in vacuum processing, for example).

さらには、疎水性シリカを生産するプロセスから排出されるガス、具体的にはシリカをシランカップリング剤などで表面処理する工程において未処理の表面処理剤を回収する際において飛散した疎水性シリカが同伴したガスが挙げられる。なお、このようなガスには、表面処理に用いた有機ケイ素化合物、具体的には、メチルトリクロロシラン、ジメチルジクロロシラン、トリメチルクロロシラン、フェニルトリクロロシラン、ジフェニルジクロロシラン、tert-ブチルジメチルクロロシラン、ビニルトリクロロシラン等のクロロシラン類やテトラメトキシシラン、メチルトリメトキシシラン、ジメチルジメトキシシラン、フェニルトリメトキシシラン、ジフェニルジメトキシシラン、o-メチルフェニルトリメトキシシラン、p-メチルフェニルトリメトキシシラン、n-ブチルトリメトキシシラン、iso-ブチルトリメトキシシラン、ヘキシルトリメトキシシラン、オクチルトリメトキシシラン、デシルトリメトキシシラン、ドデシルトリメトキシシラン、テトラエトキシシラン、メチルトリエトキシシラン、ジメチルジエトキシシラン、フェニルトリエトキシシラン、ジフェニルジエトキシシラン、iso-ブチルトリエトキシシラン、デシルトリエトキシシラン、ビニルトリエトキシシラン、γ-メタクリロキシプロピルトリメトキシシラン、γ-グリシドキシプロピルトリメトキシシラン、γ-グリシドキシプロピルメチルジメトキシシラン、γ-メルカプトプロピルトリメトキシシラン、γ-クロロプロピルトリメトキシシラン等のアルコキシシラン類、ヘキサメチルジシラザン、ヘキサエチルジシラザン、へキサプロピルジシラザン、ヘキサブチルジシラザン、ヘキサペンチルジシラザン、ヘキサヘキシルジシラザン、ヘキサシクロヘキシルジシラザン、ヘキサフェニルジシラザン、ジビニルテトラメチルジシラザン、ジメチルテトラビニルジシラザン等のシラザン類等やその誘導体(加水分解や熱による解裂などにより生じた化合物、さらにはその縮合物など)が含まれるのが一般的である。 Furthermore, gases discharged from the process of producing hydrophobic silica, specifically gases containing hydrophobic silica dispersed during recovery of untreated surface treatment agents in a process of surface treating silica with a silane coupling agent, etc., can be mentioned. Such gases include organosilicon compounds used in the surface treatment, specifically chlorosilanes such as methyltrichlorosilane, dimethyldichlorosilane, trimethylchlorosilane, phenyltrichlorosilane, diphenyldichlorosilane, tert-butyldimethylchlorosilane, and vinyltrichlorosilane, as well as tetramethoxysilane, methyltrimethoxysilane, dimethyldimethoxysilane, phenyltrimethoxysilane, diphenyldimethoxysilane, o-methylphenyltrimethoxysilane, p-methylphenyltrimethoxysilane, n-butyltrimethoxysilane, iso-butyltrimethoxysilane, hexyltrimethoxysilane, octyltrimethoxysilane, decyltrimethoxysilane, dodecyltrimethoxysilane, tetraethoxysilane, methyltriethoxysilane, dimethyldiethoxysilane, and phenyltriethoxysilane. , diphenyldiethoxysilane, iso-butyltriethoxysilane, decyltriethoxysilane, vinyltriethoxysilane, γ-methacryloxypropyltrimethoxysilane, γ-glycidoxypropyltrimethoxysilane, γ-glycidoxypropylmethyldimethoxysilane, γ-mercaptopropyltrimethoxysilane, γ-chloropropyltrimethoxysilane, and other alkoxysilanes; hexamethyldisilazane, hexaethyldisilazane, hexapropyldisilazane, hexabutyldisilazane, hexapentyldisilazane, hexahexyldisilazane, hexacyclohexyldisilazane, hexaphenyldisilazane, divinyltetramethyldisilazane, dimethyltetravinyldisilazane, and other silazanes, and derivatives thereof (compounds generated by hydrolysis or thermal cleavage, and further condensates thereof, etc.), are generally included.

または疎水性シリカを包装するプロセスにおいて粉塵として飛散した疎水性シリカの吸引回収に伴って発生したガスが挙げられる。 Or gas generated during the suction recovery of hydrophobic silica that has been dispersed as dust during the packaging process.

また含まれる疎水性シリカは特に限定なく、如何なるシリカであってもよいが、粒径やかさ密度が小さく、ガスに同伴しやすい点で、疎水性のフュームドシリカに対して適用することが好ましい。 There are no particular limitations on the hydrophobic silica contained, and any type of silica may be used, but it is preferable to use hydrophobic fumed silica, which has a small particle size and bulk density and is easily entrained in gas.

以下、上記のようにして生じる疎水性シリカを含む廃ガスを処理する本発明を更に具体的に説明するため、添付図面を参照しつつ説明を行うが、本発明はこれらの添付図面に限定されるものではない。 The present invention for treating waste gas containing hydrophobic silica produced as described above will be explained in more detail below with reference to the attached drawings, but the present invention is not limited to these drawings.

本発明の処理方法において用いられる処理設備(図1参照)は、バーナー1および燃焼室2とを有する燃焼炉8で構成される。さらに当該燃焼炉8は、燃焼処理によって生じた高温のガスやシリカ等を冷却するための冷却室3を備えることが一般的である。 The processing equipment used in the processing method of the present invention (see FIG. 1) is composed of a combustion furnace 8 having a burner 1 and a combustion chamber 2. Furthermore, the combustion furnace 8 generally includes a cooling chamber 3 for cooling the high-temperature gas and silica generated by the combustion process.

燃焼処理されたシリカが炉内をスムースに移動していきやすいという観点等から、このような燃焼炉では、バーナー1の下方に燃焼室2を有し、さらにその下方に冷却室3が設けられる構造となっている。 In order to facilitate smooth movement of the burned silica through the furnace, this type of combustion furnace is designed with a combustion chamber 2 below the burner 1, and a cooling chamber 3 below that.

バーナー1は燃料ガスおよび酸素または空気を投入することで、火炎が形成される。使用する燃料ガスは特に制限されないが、取り扱い性の観点から水素を使用することが好ましい。 A flame is formed in burner 1 by introducing fuel gas and oxygen or air. There are no particular restrictions on the fuel gas used, but it is preferable to use hydrogen from the standpoint of ease of handling.

疎水性シリカを含む廃ガスは、バーナー1で形成される火炎により、疎水性シリカの有する有機基(表面処理剤に由来する)が燃焼して、二酸化炭素や水等となってシリカから離脱し、シリカ表面に存在する基がシラノール基(さらにはこれが脱水縮合した状態)へ変換されることで、親水性シリカとなる。火炎温度は、このような燃焼反応が生じる範囲に設定されていればよいが、一般的には1,000℃以上である。 In the waste gas containing hydrophobic silica, the organic groups (derived from the surface treatment agent) of the hydrophobic silica are burned by the flame formed by burner 1, becoming carbon dioxide and water, etc., which leave the silica, and the groups present on the silica surface are converted to silanol groups (which are further dehydrated and condensed), turning it into hydrophilic silica. The flame temperature may be set within a range in which such a combustion reaction occurs, but is generally 1,000°C or higher.

図1に示す態様では、燃焼炉8へ廃ガスを導入するための廃ガス導入口4をバーナー内部に設けているが、導入された廃ガスがバーナー火炎と接触するような流れを形成できるのであれば、燃焼室2の天井や側壁に設けてもよい。 In the embodiment shown in FIG. 1, the waste gas inlet 4 for introducing waste gas into the combustion furnace 8 is provided inside the burner, but it may also be provided on the ceiling or side wall of the combustion chamber 2 as long as a flow can be formed in which the introduced waste gas comes into contact with the burner flame.

また前述のように、疎水性シリカを含む廃ガスは、このシリカの疎水化に用いた有機ケイ素化合物やその誘導体を含む場合も少なくない。ここで、このような有機ケイ素化合物も通常は燃焼させるとシリカを生じるため、上記のようにして廃ガスをバーナー火炎で燃焼処理すると、同時に当該有機ケイ素化合物もシリカ(親水性シリカ)となる。そして、このように有機ケイ素化合物の燃焼で生じた親水性シリカも、廃ガスに含まれていた疎水性シリカから燃焼処理により生じた親水性シリカと同じものとして取り扱える。 As mentioned above, waste gas containing hydrophobic silica often contains the organosilicon compound or its derivatives used to make the silica hydrophobic. Since such organosilicon compounds also usually produce silica when burned, when the waste gas is burned with a burner flame as described above, the organosilicon compound also becomes silica (hydrophilic silica). The hydrophilic silica produced by the combustion of organosilicon compounds in this way can be treated as the same as the hydrophilic silica produced by the combustion process from the hydrophobic silica contained in the waste gas.

即ち、廃ガスを燃焼処理に供することにより、疎水性シリカを親水性シリカに変換できるとともに、ガス中の有機ケイ素化合物も燃焼処理により無害化でき、さらには有機ケイ素化合物処理のための追加の工程も必要がない。 In other words, by subjecting the waste gas to combustion treatment, hydrophobic silica can be converted to hydrophilic silica, and the organosilicon compounds in the gas can be rendered harmless by the combustion treatment, eliminating the need for an additional process for treating the organosilicon compounds.

なお当然のことながら、有機ケイ素化合物以外の物質でも可燃性物質であれば同時に燃焼するから、その燃焼生成物が無害であれば、この工程で同時に無害化できる。例えば、前記表面処理を有機溶媒を用いる湿式法で行った場合、処理後の乾燥工程等において当該有機溶媒が合わせて排出される可能性があるが、多くの有機溶媒は燃焼により無害化できる。 Naturally, flammable substances other than organosilicon compounds will also burn at the same time, and if the combustion products are harmless, they can be rendered harmless in this process. For example, if the surface treatment is performed using a wet method that uses an organic solvent, the organic solvent may be discharged during the drying process after treatment, but many organic solvents can be rendered harmless by combustion.

バーナー1で燃焼処理した生じた親水性シリカは燃焼炉内を通過する際に該燃焼炉内壁へ付着しやすい。そのため、シリカの堆積による燃焼炉内の閉塞を発生させやすく、頻繁な装置のメンテナンスが必要となってしまう。従って、連続的に燃焼処理を行うためには燃焼炉内壁へのシリカ付着、堆積を防止する技術を採用することが好ましい。 The hydrophilic silica produced by the combustion process in burner 1 tends to adhere to the inner walls of the combustion furnace as it passes through the furnace. This makes it easy for the inside of the furnace to become clogged due to silica accumulation, necessitating frequent maintenance of the equipment. Therefore, in order to perform the combustion process continuously, it is preferable to employ technology that prevents silica from adhering and accumulating on the inner walls of the combustion furnace.

当該技術としては、例えば、燃焼室2の壁面に設けた旋回ガス吹き出し口6より旋回ガスを導入し、燃焼室内壁に旋回流を生じさせた状態で燃焼処理することで、燃焼室内壁へのシリカ付着、堆積を防止する方法がある。 One example of this technology is a method of preventing silica from adhering to and accumulating on the combustion chamber walls by introducing swirling gas from swirling gas outlets 6 provided on the wall surface of the combustion chamber 2 and performing combustion processing while generating a swirling flow on the combustion chamber walls.

導入する旋回ガスは、通常は不活性ガスまたは空気であればよく、経済性の観点から窒素、空気が好適である。 The swirling gas introduced is usually an inert gas or air, with nitrogen and air being preferred from an economical standpoint.

旋回流を生じさせる方法についての制限は特にないが、例えば、燃焼室内壁に旋回ガス吹き出し口6を設け、そこから旋回ガスを導入する方法がある。 There are no particular limitations on the method for generating the swirling flow, but one method is to provide a swirling gas outlet 6 on the combustion chamber wall and introduce the swirling gas from there.

当該方法を図2を参照して説明する。この方法において、旋回ガス吹き出し口6は上面から見て、0°、90°、180°、270°の少なくとも4方向に設けることが好ましい。また、燃焼室2の高さ方向の全体に旋回流を生じさせるため、高さ方向の異なる位置に複数の旋回ガス吹き出し口を設けることが好ましい。また、異なる旋回ガス吹き出し口から導入される旋回ガス同士の干渉を避けることも好ましい。これらを同時に達成するため、隣り合った旋回ガス吹き出し口は、高さ方向が異なる位置に設けることが特に好ましく、例えば上記した4つの方向に旋回ガス吹き出し口を設ける態様においては、0°、180°の投入口と90°、270°の投入口は、互いに高さ方向の異なる位置に設けることが好ましい。 This method will be described with reference to FIG. 2. In this method, it is preferable to provide the swirling gas outlets 6 in at least four directions, 0°, 90°, 180°, and 270°, as viewed from above. In addition, in order to generate a swirling flow throughout the entire height of the combustion chamber 2, it is preferable to provide multiple swirling gas outlets at different positions in the height direction. It is also preferable to avoid interference between the swirling gases introduced from different swirling gas outlets. In order to achieve these simultaneously, it is particularly preferable to provide adjacent swirling gas outlets at positions in different height directions. For example, in an embodiment in which swirling gas outlets are provided in the four directions described above, it is preferable to provide the 0° and 180° inlets and the 90° and 270° inlets at different positions in the height direction.

燃焼室外壁の接線に対する旋回ガス吹き出し口6の角度θは、燃焼炉内に旋回流を生じさせることが可能な範囲で適宜設定すればよいが、当該角度θが大きすぎる場合、燃焼室壁面近傍で旋回流が発生し難く、燃焼室壁面へのシリカ付着防止効果が弱くなることから、旋回ガス吹き出し口6の角度θは10~40°であることが好ましく、20~30°であることがより好ましい。 The angle θ of the swirling gas outlet 6 relative to the tangent of the outer wall of the combustion chamber may be set appropriately within a range that allows a swirling flow to be generated within the combustion furnace, but if the angle θ is too large, it is difficult to generate a swirling flow near the wall of the combustion chamber, and the effect of preventing silica adhesion to the wall of the combustion chamber is weakened. Therefore, the angle θ of the swirling gas outlet 6 is preferably 10 to 40°, and more preferably 20 to 30°.

旋回ガス吹き出し口6から燃焼室内に導入するガスの流速は、廃ガス中に含まれる疎水性シリカ量及びその付着性に応じて適宜設定すればよいが、ガス線速が遅いと、燃焼室内壁へのシリカ付着防止効果が弱くなり、ガス線速が速いと、燃焼室内壁の摩耗が進行することから、ガス流速は60~90Nm/s程度が好ましい。 The flow rate of the gas introduced into the combustion chamber from the swirling gas outlet 6 may be set appropriately depending on the amount of hydrophobic silica contained in the exhaust gas and its adhesion. However, if the gas linear velocity is slow, the effect of preventing silica adhesion to the combustion chamber inner wall will be weakened, and if the gas linear velocity is fast, wear of the combustion chamber inner wall will progress, so the gas flow rate is preferably about 60 to 90 Nm/s.

旋回ガス吹き出し口6の内径およびガス旋回ガス吹き出し口数は燃焼室の内径、高さ等に応じて適宜設定すればよい。 The inner diameter of the swirling gas outlet 6 and the number of gas swirling gas outlets may be set appropriately depending on the inner diameter, height, etc. of the combustion chamber.

本発明においては、上記のようにして燃焼処理することにより高温のガスが発生する。前記したように、このような高温のガスは一般に冷却室3で冷却されるが、本発明の処理方法において廃ガスに含まれるシリカは、この冷却室3の内壁に付着してしまい、運転トラブル等の原因になる場合がある。 In the present invention, high-temperature gas is generated by the combustion treatment as described above. As mentioned above, such high-temperature gas is generally cooled in the cooling chamber 3, but in the treatment method of the present invention, the silica contained in the waste gas adheres to the inner wall of this cooling chamber 3, which may cause operational problems.

そこで、本発明の処理方法においては当該冷却室3の壁面に水を流化させることでぬれ壁を形成しながら実施することが好ましい。濡れ壁を形成することで、冷却室内壁へのシリカ付着を防止すると同時に、流化させる水により燃焼処理したシリカおよび廃ガスを冷却させる。濡れ壁を採用すると、同時に冷却室内壁を保護する効果も得られる。 Therefore, it is preferable to carry out the treatment method of the present invention while forming wet walls by fluidizing the water on the wall surface of the cooling chamber 3. By forming wet walls, silica adhesion to the inner wall of the cooling chamber is prevented, and at the same time, the fluidized water cools the silica and waste gas that have been combusted. The use of wet walls also has the effect of protecting the inner wall of the cooling chamber.

ぬれ壁に流化させる水量は、燃焼処理で生じたシリカおよびガスを、機器の設計温度等を考慮した温度まで冷却するために必要な量とすればよい。 The amount of water to be added to the wetted wall should be the amount necessary to cool the silica and gases produced by the combustion process to a temperature that takes into account the design temperature of the equipment, etc.

またぬれ壁を用いる方法以外で、燃焼処理後の廃ガスを水と接触させる方法としては、スクラバー、棚段塔、充填塔などの方法が知られてり、これらを単独で、或いは適宜組み合わせて採用してもよい。 In addition to the method using a wetted wall, methods such as scrubbers, plate towers, and packed towers are known as methods for contacting waste gas after combustion treatment with water, and these may be used alone or in appropriate combination.

上記のように焼成処理に供したシリカを含む廃ガスと水を接触させると、焼成により親水化しているシリカは水に懸濁してシリカスラリーを生じる。当該シリカスラリーはタンク等に送液された後、フィルタープレス等の脱水機等により固液分離され脱水処理してシリカケーキとすればよい。なおこの際、燃焼炉出口等からタンク等への送液に必要な水を追加投入してもよい。生じたシリカケーキの処分方法は、公知の方法を適宜採用すればよい。 When the waste gas containing silica that has been subjected to the calcination treatment as described above is brought into contact with water, the silica that has been rendered hydrophilic by calcination is suspended in the water to produce a silica slurry. The silica slurry is sent to a tank or the like, and then subjected to solid-liquid separation and dehydration treatment using a dehydrator such as a filter press to produce a silica cake. At this time, additional water may be added from the combustion furnace outlet or the like as needed to send the liquid to the tank or the like. The resulting silica cake can be disposed of by any known method as appropriate.

一方、燃焼処理した廃ガスは、有機ケイ素化合物等の可燃性物質は除去されており、さらに上記のような水との接触でシリカ等の固形分も除去されているが、さらに該廃ガスの出所に応じて様々な物質を含む可能性があり、そのまま大気放出はできない場合もある。そのような場合は、含まれる物質に応じて更なる除害処理を行った上で、大気放出すればよい。 On the other hand, combustible substances such as organosilicon compounds have been removed from waste gas that has been combusted, and solids such as silica have also been removed by contact with water as described above. However, depending on the source of the waste gas, it may still contain various substances, and it may not be possible to release it directly into the atmosphere. In such cases, it is sufficient to carry out further detoxification treatment depending on the substances contained before releasing it into the atmosphere.

上記したような原理に基づき、本発明においては、疎水性シリカの廃棄方法も提供される。例えば、製造装置の清掃や製造品目の切り替えやなど様々な理由で廃棄すべき疎水性シリカが生じることがある。この場合、該廃棄疎水性シリカはいったんホッパー等に貯蔵されるが、該疎水性シリカを粉体輸送用の空気または窒素を用いて気送すれば、そのガスは前述した「疎水性シリカを含む廃ガス」と同じものとして扱うことができる。従って、これをバーナー1へ送って燃焼処理するなど、上述した方法と同様の処理に供すれば、廃棄対象の疎水性シリカをシリカケーキとすることが可能である。水を含むシリカケーキは、粉末状の疎水性シリカよりも遙かに扱いやすいため、その後の処理が容易となる。 Based on the above-mentioned principle, the present invention also provides a method for disposing of hydrophobic silica. For example, hydrophobic silica to be disposed of may be generated for various reasons, such as cleaning of manufacturing equipment or switching of manufacturing items. In this case, the disposed hydrophobic silica is temporarily stored in a hopper or the like, but if the hydrophobic silica is transported using air or nitrogen for powder transportation, the gas can be treated as the same as the above-mentioned "waste gas containing hydrophobic silica". Therefore, if this is sent to burner 1 and subjected to the same treatment as the above-mentioned method, the hydrophobic silica to be disposed of can be made into silica cake. Silica cake containing water is much easier to handle than powdered hydrophobic silica, making subsequent treatment easier.

本発明における上記したような原理は、ガス状の有機ケイ素化合物の処理に応用することも可能である。即ち、疎水性シリカが含まれていないが有機ケイ素化合物が含まれる廃ガスであれば、燃焼による疎水性シリカの親水化が生じないだけで、有機ケイ素化合物の燃焼等の他の現象は全て生じうるため、同様の処理により最終的に無害化されたガスとシリカケーキへとできる。このようなガスとしては、例えばシリカの表面処理に用いた未反応の有機ケイ素化合物や有機ケイ素化合物を充填した容器等のパージガスが挙げられる(疎水性シリカを事実上含まないもの)。有機ケイ素化合物の具体例は前記した化合物と同様である。 The above-mentioned principle of the present invention can also be applied to the treatment of gaseous organosilicon compounds. That is, if the waste gas does not contain hydrophobic silica but does contain organosilicon compounds, the hydrophobic silica will not be hydrophilized by combustion, but all other phenomena such as the combustion of the organosilicon compounds may occur, and the gas can be finally detoxified and silica cake can be obtained by similar treatment. Examples of such gases include unreacted organosilicon compounds used in the surface treatment of silica and purge gases from containers filled with organosilicon compounds (which do not actually contain hydrophobic silica). Specific examples of organosilicon compounds are the same as those mentioned above.

さらには、有機ケイ素化合物に限らず、燃焼して酸化物を生じる有機金属化合物を含む各種の廃ガスへの適用もできる。 Furthermore, it can be applied to various waste gases, including organometallic compounds that produce oxides when burned, in addition to organosilicon compounds.

1:バーナー
2:燃焼室
3:冷却室
4:廃ガス導入口
5:旋回ガス入口
6:旋回ガス吹き出し口
7:冷却水入口
8:燃焼炉
1: Burner 2: Combustion chamber 3: Cooling chamber 4: Waste gas inlet 5: Swirling gas inlet 6: Swirling gas outlet 7: Cooling water inlet 8: Combustion furnace

Claims (5)

疎水性シリカを含む廃ガスの処理方法であって、当該廃ガスを、バーナーとバーナー下方に設けられた燃焼室を有する燃焼炉で燃焼処理した後、水と接触させる工程を含み、前記燃焼室中に旋回流を生じさせた状態で燃焼処理を行うことを特徴とする前記廃ガスの処理方法。 A method for treating waste gas containing hydrophobic silica, comprising a step of combusting the waste gas in a combustion furnace having a burner and a combustion chamber provided below the burner, and then contacting the waste gas with water, characterized in that the combustion treatment is carried out while generating a swirling flow in the combustion chamber . 前記燃焼室の下方に冷却室が設けられており、当該冷却室の壁面に水を流下させた状態で燃焼処理を行う、請求項1記載の前記廃ガスの処理方法。 2. The method for treating said exhaust gas according to claim 1, further comprising the step of: providing a cooling chamber below said combustion chamber; and causing water to flow down along the wall surface of said cooling chamber to carry out the combustion treatment. 前記廃ガスが、有機ケイ素化合物を含む廃ガスである、請求項1または2記載の前記廃ガスの処理方法。 3. The method for treating said waste gas according to claim 1, wherein said waste gas contains an organosilicon compound. 前記疎水性シリカが、フュームドシリカである請求項1乃至3いずれか1項に記載の前記廃ガスの処理方法。 4. The method for treating said waste gas according to claim 1, wherein said hydrophobic silica is fumed silica. 疎水性シリカの廃棄方法であって、
バーナーとバーナー下方に設けられた燃焼室を有する燃焼炉に、廃棄対象とする疎水性シリカを気送して当該炉内で燃焼処理する工程、
燃焼処理に供されたシリカを含むガスを水と接触させて、シリカを水へ懸濁させてスラリーとする工程、及び
シリカスラリーを固液分離に供してシリカケーキを得る工程、
をこの順に含んでなり、前記燃焼室中に旋回流を生じさせた状態で燃焼処理を行うことを特徴とする疎水性シリカの廃棄方法。
1. A method for disposing of hydrophobic silica, comprising the steps of:
A step of pneumatically transporting the hydrophobic silica to be disposed of in a combustion furnace having a burner and a combustion chamber provided below the burner, and combusting the hydrophobic silica in the furnace;
a step of contacting the silica-containing gas subjected to the combustion treatment with water to suspend the silica in the water to obtain a slurry; and a step of subjecting the silica slurry to solid-liquid separation to obtain a silica cake.
and performing a combustion treatment in a state where a swirling flow is generated in the combustion chamber .
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Publication number Priority date Publication date Assignee Title
JP2000279737A (en) 1999-03-29 2000-10-10 Air Liquide Japan Ltd Cleaning dust collector and exhaust gas treatment equipment
JP2001302228A (en) 2000-04-21 2001-10-31 Shin Etsu Chem Co Ltd Method for producing hydrophobic silicon dioxide fine powder
JP2002069330A (en) 2000-08-31 2002-03-08 Shin Etsu Chem Co Ltd Method for producing hydrophobic silicon dioxide fine powder
JP2008161861A (en) 2006-12-05 2008-07-17 Ebara Corp Combustion exhaust gas treatment equipment

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DE4240741A1 (en) * 1992-12-03 1994-06-09 Wacker Chemie Gmbh Process for the hydrophobization of fumed silica

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000279737A (en) 1999-03-29 2000-10-10 Air Liquide Japan Ltd Cleaning dust collector and exhaust gas treatment equipment
JP2001302228A (en) 2000-04-21 2001-10-31 Shin Etsu Chem Co Ltd Method for producing hydrophobic silicon dioxide fine powder
JP2002069330A (en) 2000-08-31 2002-03-08 Shin Etsu Chem Co Ltd Method for producing hydrophobic silicon dioxide fine powder
JP2008161861A (en) 2006-12-05 2008-07-17 Ebara Corp Combustion exhaust gas treatment equipment

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