JP6959471B1 - Titanium component recovery method, titanium oxide manufacturing method and alkali metal titanate manufacturing method - Google Patents

Titanium component recovery method, titanium oxide manufacturing method and alkali metal titanate manufacturing method Download PDF

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JP6959471B1
JP6959471B1 JP2021108815A JP2021108815A JP6959471B1 JP 6959471 B1 JP6959471 B1 JP 6959471B1 JP 2021108815 A JP2021108815 A JP 2021108815A JP 2021108815 A JP2021108815 A JP 2021108815A JP 6959471 B1 JP6959471 B1 JP 6959471B1
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誠一郎 谷
松秀 堀川
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Toho Titanium Co Ltd
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Abstract

【解決課題】チタン化合物を含む排液から、チタン成分を回収する方法又は酸化チタンを製造方法において、中和剤として、水酸化カルシウムを用いても、得られる回収チタン成分又は酸化チタン中のカルシウム含有量が少ないチタン成分の回収方法又は酸化チタンの製造方法を提供すること。【解決手段】チタン化合物を含む排液からチタン成分を回収するチタン成分の回収方法であって、該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3)と、を有すること、を特徴とするチタン成分の回収方法。【選択図】図1PROBLEM TO BE SOLVED: To recover a titanium component or calcium in titanium oxide obtained by using calcium hydroxide as a neutralizing agent in a method for recovering a titanium component from a effluent containing a titanium compound or a method for producing titanium oxide. To provide a method for recovering a titanium component having a low content or a method for producing titanium oxide. SOLUTION: This is a method for recovering a titanium component from a effluent containing a titanium compound, wherein the effluent containing the titanium compound is brought into contact with water to hydrolyze the titanium compound (1). , The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 1.5 or more and less than 2.5, and then the primary neutralizing treatment is performed. The treated solution subjected to the sum treatment is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is added. In the step (2) of obtaining an agglomerate of titanium hydroxide by performing an agglomeration treatment for aggregating, and in the subsequent stage after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the agglomerate of titanium hydroxide to obtain titanium hydroxide. A method for recovering a titanium component, which comprises the step (3) of obtaining an acid-treated product of the agglomerates of the above. [Selection diagram] Fig. 1

Description

本発明は、チタン成分の回収方法、酸化チタンの製造方法及びチタン酸アルカリ金属の製造方法に関する。 The present invention relates to a method for recovering a titanium component, a method for producing titanium oxide, and a method for producing an alkali metal titanate.

従来、プロピレンなどのオレフィン類の重合が、マグネシウム、チタン、電子供与性化合物およびハロゲン等を含有するオレフィン類重合用固体触媒成分を用いて行われており、これ等固体触媒成分は、例えば、溶液状のマグネシウム化合物と溶液状のチタン化合物とを必要に応じ電子供与性化合物の存在下において接触させることで、作製されている。 Conventionally, polymerization of olefins such as propylene has been carried out using solid catalyst components for olefin polymerization containing magnesium, titanium, electron donating compounds, halogens and the like, and these solid catalyst components are, for example, solutions. It is produced by contacting a magnesium compound in the form of a magnesium compound and a titanium compound in the form of a solution in the presence of an electron donating compound, if necessary.

このようなオレフィン類重合用固体触媒成分を調製する際や、当該固体触媒成分からオレフィン類重合用触媒を調製する際に、固体触媒成分に担持されなかった余剰のチタン化合物や調製時の副反応等で生成したその他のチタン化合物を含有する排液が生じてしまう。 When preparing such a solid catalyst component for olefin polymerization or when preparing a catalyst for olefin polymerization from the solid catalyst component, excess titanium compounds not supported by the solid catalyst component and side reactions at the time of preparation Drainage containing other titanium compounds produced by the above will occur.

従来は、減圧蒸留により廃溶液からチタン化合物を回収していたが、この方法では蒸留母液またはトレーに固形物が析出し、蒸留釜残液の排出が困難になり、塔内差圧の発生等により蒸留の継続が困難になるため、チタン化合物の回収を充分に行わないまま蒸留を停止し、蒸留釜残液を廃棄していた。 In the past, the titanium compound was recovered from the waste solution by vacuum distillation, but with this method, solid matter precipitates in the distillation mother liquor or tray, making it difficult to discharge the residual liquid in the distillation pot, and generating differential pressure in the column. As a result, it becomes difficult to continue the distillation. Therefore, the distillation was stopped without sufficiently recovering the titanium compound, and the residual liquid in the distillation pot was discarded.

しかしながら、資源の有効利用、廃棄物の削減等の観点から、回収しきれなかったチタン化合物が含まれる蒸留釜残液から、さらにチタン化合物を回収する方法、回収したチタン化合物を再利用する方法等が求められるようになっている。 However, from the viewpoint of effective use of resources, reduction of waste, etc., a method of further recovering the titanium compound from the residual liquid of the distillation pot containing the titanium compound that could not be recovered, a method of reusing the recovered titanium compound, etc. Has come to be required.

これらチタン化合物を含有する蒸留釜残液からチタン化合物を回収する方法としては、例えば、特許文献1において、ポリマー製造用触媒成分を調製する際に発生するチタン化合物を含む廃溶液からチタン化合物の一部をフラッシュ蒸留回収した後、回収残分と水とを接触させ、回収残分中のチタン化合物を加水分解し、水相を分離回収後に塩基で中和し、凝集剤等により固形物を凝集・沈降させ、該沈降物を回収後、含水量を減らしてプレスケーキとし、これらプレスケーキを焼成して粗酸化チタンを回収する方法が提案されている。 As a method for recovering the titanium compound from the residual liquid of the distillation pot containing these titanium compounds, for example, in Patent Document 1, one of the titanium compounds from a waste solution containing the titanium compound generated when a catalyst component for polymer production is prepared. After the part is flash-distilled and recovered, the recovered residue is brought into contact with water, the titanium compound in the recovered residue is hydrolyzed, the aqueous phase is separated and recovered, neutralized with a base, and the solid matter is agglomerated with a flocculant or the like. -A method has been proposed in which the sediment is settled, the sediment is recovered, the water content is reduced to obtain a press cake, and these press cakes are fired to recover the crude titanium oxide.

上記分離回収後の水相を中和する際に用いる塩基として、通常は、安価かつ取り扱いの容易なアンモニア水や水酸化カルシウムが好適に用いられていた。 As the base used for neutralizing the aqueous phase after the separation and recovery, usually, inexpensive and easy-to-handle ammonia water or calcium hydroxide has been preferably used.

しかしながら、特許文献1記載の方法では回収した粗酸化チタン中に窒素やカルシウムが混入する等して純度の高いチタン化合物を回収し得ない。 However, with the method described in Patent Document 1, a titanium compound having high purity cannot be recovered because nitrogen or calcium is mixed in the recovered crude titanium oxide.

そこで、特許文献2の実施例では、オレフィン類重合用固体触媒成分を調製した際に発生した、四塩化チタン、ジエトキシマグネシウム、トルエン及びブタンを含む排液を、水と接触させて加水分解を施し、次いで、pHが2になるように水酸化ナトリウムを加えて一次中和処理を施し、次いで、pHが6.5になるように水酸化ナトリウムを加えて二次中和処理を施して、酸化チタンを凝集させることにより、酸化チタンを得ている。 Therefore, in the examples of Patent Document 2, the effluent containing titanium tetrachloride, diethoxymagnesium, toluene and butane generated when the solid catalyst component for olefin polymerization was prepared was brought into contact with water for hydrolysis. Then, sodium hydroxide was added so that the pH became 2, and the primary neutralization treatment was performed. Then, sodium hydroxide was added so that the pH became 6.5, and the secondary neutralization treatment was performed. Titanium oxide is obtained by aggregating titanium oxide.

特開2001−261340号公報Japanese Unexamined Patent Publication No. 2001-261340 特開2018−80086号公報Japanese Unexamined Patent Publication No. 2018-8806

特許文献2の方法では、アナターゼ型の酸化チタンに代えてルチル型の酸化チタンが生成し易くなり、高純度なチタン化合物が高収率で得られている。 In the method of Patent Document 2, rutile-type titanium oxide is easily produced instead of anatase-type titanium oxide, and a high-purity titanium compound is obtained in a high yield.

ここで、特許文献2の段落番号0035に「高純度な酸化チタンを得る上では、得られる酸化チタン中に窒素やカルシウム等の異物の混入を抑制するために、中和剤としてアンモニア水や水酸化カルシウム等を使用しないことが好ましい。」と記載されているように、特許文献2の実施例では、高純度なチタン化合物を得るために、中和剤として、水酸化ナトリウムを用いている。 Here, in paragraph No. 0035 of Patent Document 2, "In order to obtain high-purity titanium oxide, in order to suppress the mixing of foreign substances such as nitrogen and calcium in the obtained titanium oxide, ammonia water or water as a neutralizing agent is used. As described in "It is preferable not to use calcium oxide or the like.", In the examples of Patent Document 2, sodium hydroxide is used as a neutralizing agent in order to obtain a high-purity titanium compound.

ところが、工業的に、排水処理コストを抑制するためには、中和剤には、水酸化カルシウム又は酸化カルシウムを用いる必要がある。そこで、本発明者等が検討行ったところ、特許文献2の実施例の方法において、用いられている中和剤を、水酸化ナトリウムから、水酸化カルシウムに変更すると、得られる水酸化チタンの凝集物中に、低水溶性の水酸化カルシウム又は炭酸カルシウムが残存してしまい、その後の洗浄によっては、カルシウム成分を除去できないことが分かった。 However, industrially, in order to suppress the wastewater treatment cost, it is necessary to use calcium hydroxide or calcium oxide as the neutralizing agent. Therefore, as a result of studies by the present inventors, when the neutralizing agent used in the method of Examples of Patent Document 2 is changed from sodium hydroxide to calcium hydroxide, aggregation of titanium hydroxide obtained is obtained. It was found that low-water-soluble calcium hydroxide or calcium carbonate remained in the substance, and the calcium component could not be removed by subsequent washing.

そして、回収酸化チタンの利用方法としては、チタン酸カアルカリ金属の製造原料として用いることが挙げられるが、回収酸化チタン中に混入されたカルシウム成分は、回収酸化チタンをチタン酸アルカリ金属の合成原料として用いた場合に、不純物であるチタン酸カルシウムの発生源となるため、回収酸化チタンには、カルシウム分の含有量が低いことが望まれる。 As a method of using the recovered titanium oxide, it can be mentioned that it is used as a raw material for producing a calcium titanate alkali metal, but the calcium component mixed in the recovered titanium oxide uses the recovered titanium oxide as a synthetic raw material for the alkali metal titanate. When used, it becomes a source of calcium titanate, which is an impurity, so it is desirable that the recovered titanium oxide has a low calcium content.

そこで、本発明の目的は、チタン化合物を含む排液、好ましくはオレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタン化合物を含む排液から、チタン成分を回収する方法又は酸化チタンを製造方法において、中和剤として、水酸化カルシウム又は酸化カルシウムを用いても、得られる回収チタン成分又は酸化チタン中のカルシウム含有量が少ないチタン成分の回収方法又は酸化チタンの製造方法を提供することにある。 Therefore, an object of the present invention is to recover the titanium component from the effluent containing the titanium compound, preferably the effluent containing the titanium compound generated when preparing the solid catalyst component for olefin polymerization or the catalyst for olefin polymerization. Even if calcium hydroxide or calcium oxide is used as a neutralizing agent in the method or the method for producing titanium oxide, the recovered titanium component obtained or the method for recovering the titanium component having a low calcium content in titanium oxide or the production of titanium oxide To provide a method.

上記技術課題を解決すべく、本発明者等が鋭意検討を行ったところ、チタン化合物を含む排液を水と接触させチタン化合物を加水分解処理し、次いで、水酸化カルシウム又は酸化カルシウムを使用して一次中和処理及び二次中和処理を施して、次いで、水酸化チタンを凝集させて生じる水酸化チタンの凝集物に、pH5.9以下の塩酸を接触させることにより、カルシウム含有量が少ない水酸化チタンの凝集物が得られることを見出し、本知見に基づいて本発明を完成するに至った。 As a result of diligent studies by the present inventors in order to solve the above technical problems, the effluent containing the titanium compound was brought into contact with water to hydrolyze the titanium compound, and then calcium hydroxide or calcium oxide was used. The calcium content is low by subjecting the primary neutralization treatment and the secondary neutralization treatment, and then contacting the aggregate of titanium hydroxide formed by aggregating titanium hydroxide with hydrochloric acid having a pH of 5.9 or less. It has been found that an agglomerate of titanium hydroxide can be obtained, and the present invention has been completed based on this finding.

すなわち、本発明は、
(1)チタン化合物を含む排液からチタン成分を回収するチタン成分の回収方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3)と、
を有すること、
を特徴とするチタン成分の回収方法;
(2)前記工程(2)を行い生じる前記水酸化チタンの凝集物の濃縮物を得た後、水酸化チタンの凝集物の濃縮物を分離し、次いで、該水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、前記水酸化チタンの凝集物の酸処理物を得る工程(3A)を有することを特徴とする(1)のチタン成分の回収方法;
(3)前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させることにより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする(2)のチタン成分の回収方法、
(4)前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物を分離し、次いで、該水酸化チタンの凝集物の沈降物から液相を除去する脱水処理を行い、水酸化チタンの凝集物の脱水処理物を得ることより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする(2)のチタン成分の回収方法;
(5)前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3B)を有することを特徴とする(1)のチタン成分の回収方法;
(6)前記水酸化チタンの凝集物の酸処理物を、6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することを特徴とする(1)〜(5)いずれかのチタン成分の回収方法;
(7)チタン化合物を含む排液から酸化チタンを製造する酸化チタンの製造方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3)と、
該水酸化チタンの凝集物の酸処理物を酸化して、酸化チタンを得る酸化工程と、
を有すること、
を特徴とする酸化チタンの製造方法;
(8)前記工程(2)を行い生じる前記水酸化チタンの凝集物の濃縮物を得た後、該水酸化チタンの凝集物の濃縮物を分離し、次いで、該水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、前記水酸化チタンの凝集物の酸処理物を得る工程(3A)を有することを特徴とする(7)のチタン成分の回収方法;
(9)前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させることにより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする(8)のチタン成分の回収方法;
(10)前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物を分離し、次いで、該水酸化チタンの凝集物の沈降物から液相を除去する脱水処理を行い、水酸化チタンの凝集物の脱水処理物を得ることより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする(8)のチタン成分の回収方法;
(11)前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3B)を有することを特徴とする(7)の酸化チタンの製造方法;
(12)前記水酸化チタンの凝集物の酸処理物を、6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することを特徴とする(7)〜(11)いずれかの酸化チタンの製造方法;
(13)(1)〜(6)いずれかのチタン成分の回収方法により回収された水酸化チタン、又は(7)〜(12)いずれかの酸化チタンの製造方法により得られた酸化チタンを原料として用いることを特徴とするチタン酸アルカリ金属の製造方法;
を提供するものである。
That is, the present invention
(1) A method for recovering a titanium component from a effluent containing a titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. Step (2) to obtain agglomerates of titanium hydroxide by performing agglomeration treatment
In the step after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the titanium hydroxide agglutination to obtain an acid-treated product of the titanium hydroxide agglutination.
To have
A method for recovering a titanium component, which is characterized by
(2) After obtaining the concentrate of the titanium hydroxide agglomerate produced by performing the step (2), the concentrate of the titanium hydroxide agglomerate is separated, and then the concentrate of the titanium hydroxide agglomerate is concentrated. The object is characterized by having a step (3A) of contacting an object with hydrochloric acid to perform acid treatment of the titanium hydroxide agglomerate to obtain an acid-treated product of the titanium hydroxide agglomerate. Titanium component recovery method;
(3) In the step (3A), the agglomerate of the titanium hydroxide produced by performing the step (2) is settled to obtain a concentrate of the agglomerate of titanium hydroxide (2). ) Titanium component recovery method,
(4) In the step (3A), after the agglomerates of the titanium hydroxide produced by performing the step (2) are settled, the settling of the agglomerates of titanium hydroxide is separated, and then the titanium hydroxide is settled. A dehydration treatment for removing the liquid phase from the precipitate of the agglomerates of titanium hydroxide is performed to obtain a dehydrated product of the agglomerates of titanium hydroxide, thereby obtaining a concentrate of the agglomerates of titanium hydroxide (1). 2) Titanium component recovery method;
(5) After the titanium hydroxide agglomerates produced by performing the step (2) are precipitated, hydrochloric acid is brought into contact with the titanium hydroxide agglomerates to bring the acid of the titanium hydroxide agglomerates into contact. The method for recovering a titanium component according to (1), which comprises a step (3B) of performing treatment to obtain an acid-treated product of agglomerates of titanium hydroxide;
(6) Titanium according to any one of (1) to (5), which comprises a washing step of washing the acid-treated product of the aggregate of titanium hydroxide with washing water of 6.0 or more and 9.0 or less. Ingredient recovery method;
(7) A method for producing titanium oxide, which produces titanium oxide from a effluent containing a titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. Step (2) to obtain agglomerates of titanium hydroxide by performing agglomeration treatment
In the step after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the titanium hydroxide agglutination to obtain an acid-treated product of the titanium hydroxide agglutination.
An oxidation step of oxidizing the acid-treated product of the titanium hydroxide agglomerate to obtain titanium oxide, and
To have
A method for producing titanium oxide, which is characterized by the above;
(8) After obtaining the concentrate of the titanium hydroxide agglomerate produced by performing the step (2), the concentrate of the titanium hydroxide agglomerate is separated, and then the titanium hydroxide agglomerate is separated. It is characterized by having a step (3A) of contacting the concentrate with hydrochloric acid to perform acid treatment of the titanium hydroxide agglomerate to obtain an acid-treated product of the titanium hydroxide agglomerate (7). How to recover the titanium component of
(9) In the step (3A), a concentrate of the titanium hydroxide agglomerates is obtained by precipitating the titanium hydroxide agglomerates produced by performing the step (2) (8). ) Titanium component recovery method;
(10) In the step (3A), after the agglomerates of the titanium hydroxide produced by performing the step (2) are settled, the settling of the agglomerates of titanium hydroxide is separated, and then the titanium hydroxide is settled. A dehydration treatment for removing the liquid phase from the precipitate of the agglomerates of titanium hydroxide is performed to obtain a dehydrated product of the agglomerates of titanium hydroxide, thereby obtaining a concentrate of the agglomerates of titanium hydroxide (1). 8) Method for recovering titanium component;
(11) After the agglomerates of titanium hydroxide produced by performing the step (2) are precipitated, hydrochloric acid is brought into contact with the agglomerates of titanium hydroxide to bring the acid of the agglomerates of titanium hydroxide. The method for producing titanium oxide according to (7), which comprises a step (3B) of performing treatment to obtain an acid-treated product of agglomerates of titanium hydroxide;
(12) The oxidation according to any one of (7) to (11), which comprises a washing step of washing the acid-treated product of the aggregate of titanium hydroxide with washing water of 6.0 or more and 9.0 or less. Titanium manufacturing method;
(13) Titanium hydroxide recovered by the method for recovering the titanium component according to any one of (1) to (6), or titanium oxide obtained by the method for producing titanium oxide according to any one of (7) to (12) as a raw material. A method for producing an alkali metal titanate, which is characterized by being used as
Is to provide.

本発明によれば、チタン化合物を含む排液、好ましくはオレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタン化合物を含む排液から、チタン成分を回収する方法又は酸化チタンを製造する方法において、中和剤として、水酸化カルシウム又は酸化カルシウムを用いても、得られる回収チタン成分又は酸化チタン中のカルシウム含有量が少ないチタン成分の回収方法又は酸化チタンの製造方法を提供することができる。 According to the present invention, a method for recovering a titanium component from a effluent containing a titanium compound, preferably a solid catalyst component for olefin polymerization or a effluent containing a titanium compound generated when a catalyst for olefin polymerization is prepared. In the method for producing titanium oxide, even if calcium hydroxide or calcium oxide is used as a neutralizing agent, the obtained recovered titanium component or the method for recovering the titanium component having a low calcium content in titanium oxide or the method for producing titanium oxide. Can be provided.

本発明のチタン成分の回収方法の形態例のフロー図である。It is a flow chart of the form example of the method of recovering a titanium component of this invention. 本発明の第一の形態のチタン成分の回収方法の形態例のフロー図である。It is a flow chart of the form example of the method of recovering the titanium component of the 1st form of this invention. 本発明の第一の形態のチタン成分の回収方法のうち、洗浄工程を行う形態例のフロー図である。It is a flow chart of the form example which performs the cleaning step among the method of recovering the titanium component of the 1st aspect of this invention. 本発明の第一の形態のチタン成分の回収方法のうち、洗浄工程を行う他の形態例のフロー図である。It is a flow chart of the other form example which performs a cleaning step among the method of recovering a titanium component of the 1st form of this invention. 本発明の第二の形態のチタン成分の回収方法の形態例のフロー図である。It is a flow chart of the form example of the method of recovering the titanium component of the 2nd form of this invention. 本発明の第二の形態のチタン成分の回収方法のうち、洗浄工程を行う形態例のフロー図である。It is a flow chart of the form example which performs the cleaning step among the method of recovering the titanium component of the 2nd aspect of this invention. 本発明の第二の形態のチタン成分の回収方法のうち、洗浄工程を行う他の形態例のフロー図である。It is a flow chart of the other form example which performs a cleaning step among the method of recovering a titanium component of the 2nd form of this invention. 実施例1で得られたチタン酸カリウムの走査型電子顕微鏡写真である。It is a scanning electron micrograph of potassium titanate obtained in Example 1. FIG. 実施例1において、比較として分析した市販のチタン酸カリウムの走査型電子顕微鏡写真である。6 is a scanning electron micrograph of commercially available potassium titanate analyzed for comparison in Example 1. 実施例2で得られたチタン酸カリウムの走査型電子顕微鏡写真である。It is a scanning electron micrograph of potassium titanate obtained in Example 2. FIG. 実施例2において、比較として分析した市販のチタン酸カリウムの走査型電子顕微鏡写真である。2 is a scanning electron micrograph of commercially available potassium titanate analyzed for comparison in Example 2.

先ず、本発明のチタン成分の回収方法について説明する。
本発明のチタン成分の回収方法は、チタン化合物を含む排液からチタン成分を回収するチタン成分の回収方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3)と、
を有すること、
を特徴とする。
First, the method for recovering the titanium component of the present invention will be described.
The method for recovering a titanium component of the present invention is a method for recovering a titanium component from a effluent containing a titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. Step (2) to obtain agglomerates of titanium hydroxide by performing agglomeration treatment
In the step after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the titanium hydroxide agglutination to obtain an acid-treated product of the titanium hydroxide agglutination.
To have
It is characterized by.

本発明のチタン成分の回収方法について、図1を参照して説明する。なお、ここでは中和剤として水酸化カルシウムを適用した形態を例に挙げて説明するが、本発明においては、中和剤として酸化カルシウムを適用しても水酸化カルシウムを適用した場合と同様の効果が得られる。図1は、本発明のチタン成分の回収方法の形態例のフロー図である。図1中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物19を生じさせる。そして、水酸化チタンの凝集物19を生じさせた後、得られた水酸化チタンの凝集物19に塩酸14を接触させて、水酸化チタンの凝集物19の酸処理を行い、水酸化チタンの凝集物の酸処理物20を得る。 The method for recovering the titanium component of the present invention will be described with reference to FIG. Here, a form in which calcium hydroxide is applied as a neutralizing agent will be described as an example, but in the present invention, even if calcium oxide is applied as a neutralizing agent, it is the same as when calcium hydroxide is applied. The effect is obtained. FIG. 1 is a flow chart of a mode example of the method for recovering a titanium component of the present invention. In FIG. 1, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and the titanium hydroxide is coagulated to obtain the titanium hydroxide agglomerate 19. Give rise. Then, after the titanium hydroxide agglomerates 19 are generated, hydrochloric acid 14 is brought into contact with the obtained titanium hydroxide agglomerates 19 to perform acid treatment of the titanium hydroxide agglomerates 19 to obtain titanium hydroxide. An acid-treated product 20 of the agglomerates is obtained.

本発明のチタン成分の回収方法において、チタン成分の回収方法が施される対象は、チタン化合物を含む排液であり、チタン化合物を含むものであれば、特に制限されない。チタン化合物を含む排液としては、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生する「チタンを含む排液」が好ましい。 In the method for recovering a titanium component of the present invention, the target to which the method for recovering a titanium component is applied is a effluent containing a titanium compound, and is not particularly limited as long as it contains a titanium compound. As the effluent containing the titanium compound, the "drainage containing titanium" generated when the solid catalyst component for olefin polymerization or the catalyst for olefin polymerization is prepared is preferable.

本発明のチタン成分の回収方法において、チタン化合物を含む排液が、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタンを含む排液の場合、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒としては、オレフィン類の重合に供されるチタン成分を含む固体触媒成分又は触媒であれば特に制限されず、例えば、ポリオレフィン製造に用いられるチーグラーナッタ触媒、メタロセン触媒、ポストメタロセン、ポリエチレンテレフタレート製造用の固体状チタン触媒等の触媒や、これ等の触媒を構成する固体触媒成分から選ばれる1種以上が挙げられ、これらの中でも、ポリオレフィン製造に用いられるチーグラーナッタ触媒、メタロセン触媒及びポストメタロセン触媒やこれ等の触媒を構成する固体触媒成分から選ばれる1種以上が好ましく、チーグラーナッタ触媒またはチーグラーナッタ触媒を構成する固体触媒成分がより好ましい。 In the method for recovering a titanium component of the present invention, when the effluent containing a titanium compound is a solid catalyst component for olefin polymerization or a effluent containing titanium generated when a catalyst for olefin polymerization is prepared, it is used for olefin polymerization. The solid catalyst component or the catalyst for olefin polymerization is not particularly limited as long as it is a solid catalyst component or catalyst containing a titanium component used for the polymerization of olefins. , Post-metallocene, catalysts such as solid titanium catalysts for the production of polyethylene terephthalates, and one or more selected from the solid catalyst components constituting these catalysts, among these, the Ziegler-Natta catalyst used for the production of polyolefins. , Metallocene catalysts and post-metallocene catalysts, and one or more selected from the solid catalyst components constituting these catalysts are preferable, and the Ziegler-Natta catalyst or the solid catalyst component constituting the Ziegler-Natta catalyst is more preferable.

チーグラーナッタ触媒又はチーグラーナッタ触媒を構成する固体触媒成分としては、上記のうち、マグネシウム化合物、チタン化合物及びハロゲン化合物、更に、必要に応じ電子供与性化合物を、接触させることにより調製されるオレフィン類重合用固体触媒成分が好適である。 As the solid catalyst component constituting the Ziegler-Natta catalyst or the Ziegler-Natta catalyst, among the above, olefin polymerization prepared by contacting a magnesium compound, a titanium compound and a halogen compound, and if necessary, an electron donating compound. Solid catalyst components for use are suitable.

上記オレフィン類重合用固体触媒成分の調製に使用されるマグネシウム化合物としては、ハロゲンを含有するもの及びハロゲン含有化合物と接触反応させることによりハロゲン含有マグネシウム化合物に変化するものが好ましい。
このようなマグネシウム化合物としては、塩化マグネシウム等の二ハロゲン化マグネシウム、アルコキシマグネシウムハライドなどのジアルキルマグネシウム、アルキルマグネシウムハライドおよびジエトキシマグネシウム等のジアルコキシマグネシウム等から選ばれる1種以上が挙げられ、塩化マグネシウム又はジエトキシマグネシウムが好ましい。
As the magnesium compound used for preparing the solid catalyst component for olefin polymerization, those containing a halogen and those that change to a halogen-containing magnesium compound by contact reaction with the halogen-containing compound are preferable.
Examples of such magnesium compounds include one or more selected from magnesium dihalogenate such as magnesium chloride, dialkyl magnesium such as alkoxymagnesium halide, and dialkoxymagnesium such as alkylmagnesium halide and diethoxymagnesium, and magnesium chloride. Alternatively, diethoxymagnesium is preferable.

本発明のチタン成分の回収方法に係るチタン化合物としては、例えば、下記一般式(1):
Ti(OR)4−N (1)
(式中、Rは、炭化水素基、Xはハロゲン原子を示し、Xが複数存在する場合、各Xは同一であっても異なっていてもよく、Nは、0〜4の整数である。)で表されるチタン化合物が挙げられる。
Examples of the titanium compound according to the method for recovering the titanium component of the present invention include the following general formula (1):
Ti (OR) N X 4-N (1)
(In the formula, R represents a hydrocarbon group, X represents a halogen atom, and when a plurality of Xs are present, each X may be the same or different, and N is an integer of 0 to 4. ), Examples of the titanium compound.

一般式(1)で表されるチタン化合物において、Rは、炭素数1〜10の炭化水素基であることが好ましく、炭素数1〜6の炭化水素基であることがより好ましく、炭素数1〜4の炭化水素基であることがさらに好ましい。 In the titanium compound represented by the general formula (1), R is preferably a hydrocarbon group having 1 to 10 carbon atoms, more preferably a hydrocarbon group having 1 to 6 carbon atoms, and has 1 carbon atom. More preferably, it is a hydrocarbon group of ~ 4.

一般式(1)で表されるチタン化合物としては、具体的には、四塩化チタン、四フッ化チタン、四臭化チタン、四ヨウ化チタン等の四ハロゲン化チタン、メトキシチタントリクロライド、エトキシチタントリクロライド、プロポキシチタントリクロライド、N−ブトキシチタントリクロライド等のアルコキシチタントリハライド、ジメトキシチタンジクロライド、ジエトキシチタンジクロライド、ジプロポキシチタンジクロライド、ジ−N−ブトキシチタンジクロライド等のジアルコキシチタンジハライド、トリメトキシチタンクロライド、トリエトキシチタンクロライド、トリプロポキシチタンクロライド、トリ−N−ブトキシチタンクロライド等のトリアルコキシチタンハライド等のアルコキシチタンハライド等のテトラアルコキシチタンから選ばれる1種以上が挙げられる。 Specific examples of the titanium compound represented by the general formula (1) include titanium tetrahalide such as titanium tetrachloride, titanium tetrafluoride, titanium tetrabromide, and titanium tetraiodide, methoxytitanium trichloride, and ethoxy. Alkoxytitanium trihalide such as titanium trichloride, propoxytitanium trichloride, N-butoxytitanium trichloride, dimethoxytitanium dichloride, diethoxytitanium dichloride, dipropoxytitanium dichloride, dialkoxytitanium dihalide such as di-N-butoxytitanium dichloride , Trimethoxy Titanium Chloride, Triethoxy Titanium Chloride, Tripropoxy Titanium Chloride, Tri-N-Butoxy Titanium Chloride, etc. Trialkoxy Titanium Halide, etc. Alkoxy Titanium Halide, etc.

上記チタン化合物のうち、ハロゲン含有チタン化合物が好ましく、四塩化チタン、四フッ化チタン、四臭化チタン、四ヨウ化チタン等から選ばれる四ハロゲン化チタンがより好ましく、四塩化チタンがさらに好ましい。
上記チタン化合物は、炭化水素化合物またはハロゲン化炭化水素化合物などにより希釈されていてもよい。
Among the above titanium compounds, a halogen-containing titanium compound is preferable, titanium tetrahalide selected from titanium tetrachloride, titanium tetrafluoride, titanium tetrabromide, titanium tetraiodide and the like is more preferable, and titanium tetrachloride is even more preferable.
The titanium compound may be diluted with a hydrocarbon compound, a halogenated hydrocarbon compound, or the like.

オレフィン類重合用固体触媒成分の調製に使用される電子供与性化合物としては、特に限定されないが、アルコール類、フェノール類、ケトン類、アルデヒド類、カルボン酸、酸ハライド類、有機酸または無機酸のエステル類、エーテル類、酸アミド類、酸無水物、アンモニア、アミン類、ニトリル類、イソシアネート、含窒素環状化合物、含酸素環状化合物、有機ケイ素化合物等から選ばれる1種以上が挙げられる。 The electron donating compound used for preparing the solid catalyst component for olefin polymerization is not particularly limited, but includes alcohols, phenols, ketones, aldehydes, carboxylic acids, acid halides, organic acids or inorganic acids. Examples thereof include one or more selected from esters, ethers, acid amides, acid anhydrides, ammonia, amines, nitriles, isocyanates, nitrogen-containing cyclic compounds, oxygen-containing cyclic compounds, organic silicon compounds and the like.

本発明のチタン成分の回収方法において、チタン化合物を含む排液は、オレフィン類重合用固体触媒成分の調製工程において、洗浄時、加熱接触時等に使用する有機溶媒成分、具体的には、ペンタン、ヘキサン、ヘプタン、オクタン、ノナン、デカン、ドデカン、灯油、シクロペンタン、シクロヘキサン、メチルシクロペンタン、メチルシクロヘキサン、エチルシクロヘキサン、1,2−ジエチルシクロヘキサン、メチルシクロヘキセン、デカリン、ミネラルオイル等の飽和炭化水素化合物、ベンゼン、トルエン、キシレン、エチルベンゼン等の芳香族炭化水素化合物、オルトジクロルベンゼン、塩化メチレン、1,2−ジクロロベンゼン、四塩化炭素、ジクロルエタン、エチレンクロリド、クロルベンゼン、ジクロロメタン等のハロゲン化炭化水素化合物等、アルミ化合物、ケイ素化合物等から選ばれる1種以上の有機溶媒成分を含むものであってもよい。 In the method for recovering the titanium component of the present invention, the effluent containing the titanium compound is an organic solvent component used at the time of cleaning, heat contact, etc. in the step of preparing the solid catalyst component for olefin polymerization, specifically, pentane. , Hexane, heptane, octane, nonane, decane, dodecane, kerosene, cyclopentane, cyclohexane, methylcyclopentane, methylcyclohexane, ethylcyclohexane, 1,2-diethylcyclohexane, methylcyclohexene, decalin, mineral oil and other saturated hydrocarbon compounds. , Aromatic hydrocarbon compounds such as benzene, toluene, xylene, ethylbenzene, orthodichlorobenzene, methylene chloride, 1,2-dichlorobenzene, carbon tetrachloride, dichloroethane, ethylene chloride, chlorobenzene, dichloromethane and other halogenated hydrocarbons. It may contain one or more organic solvent components selected from compounds and the like, aluminum compounds, silicon compounds and the like.

本発明のチタン成分の回収方法において、チタン化合物を含む排液としては、マグネシウム化合物として塩化マグネシウム又はジエトキシマグネシウムを含み、チタン化合物としてアルコキシチタンハロゲン化合物又はハロゲン化チタン化合物を含み、更に電子供与性化合物及び有機溶媒成分を含むものが好適である。 In the method for recovering a titanium component of the present invention, the effluent containing a titanium compound contains magnesium chloride or diethoxymagnesium as a magnesium compound, an alkoxytitanium halogen compound or a titanium halide compound as a titanium compound, and further electron donating property. Those containing a compound and an organic solvent component are preferable.

本発明のチタン成分の回収方法において、チタン化合物を含む排液は、種々の反応等で生じたチタン化合物を含む。チタン化合物を含む排液は、好ましくはオレフィン類重合用固体触媒成分やオレフィン類重合用触媒の調製時に生じる排液であり、このような排液は、固体触媒成分に担持されなかったチタン化合物やその調製工程における反応などで新たに生じたその他のチタン化合物を含む。本発明のチタン成分の回収方法において、チタン化合物を含む排液は、チタン化合物を、0.01〜35.0質量%を含むものが好ましく、0.05〜10.0質量%含むものがより好ましく、0.10〜5.0質量%含むものがさらに好ましい。 In the method for recovering the titanium component of the present invention, the effluent containing the titanium compound contains the titanium compound generated by various reactions and the like. The effluent containing a titanium compound is preferably a effluent generated during the preparation of a solid catalyst component for olefin polymerization or a catalyst for olefin polymerization, and such effluent is a titanium compound or a effluent that is not supported by the solid catalyst component. It contains other titanium compounds newly generated by the reaction in the preparation process. In the method for recovering the titanium component of the present invention, the drainage containing the titanium compound preferably contains 0.01 to 3.0% by mass of the titanium compound, more preferably 0.05 to 10.0% by mass. It is preferable, and the one containing 0.10 to 5.0% by mass is more preferable.

本発明に係るチタン成分の回収方法は、チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)を有する。工程(1)において、加水分解方法としては、特に制限されず、排水を受水する受水槽中で別途注入した水と接触させる方法等が挙げられる。 The method for recovering a titanium component according to the present invention includes a step (1) in which a effluent containing a titanium compound is brought into contact with water to hydrolyze the titanium compound. In the step (1), the hydrolysis method is not particularly limited, and examples thereof include a method of bringing the wastewater into contact with water separately injected in the water receiving tank.

工程(1)において、チタン化合物がハロゲン化チタンである場合には、チタン化合物を含む排液を水と接触させることにより、チタン化合物が加水分解されて、ハロゲン化水素及び水酸化チタンを生成する。 In the step (1), when the titanium compound is titanium halide, the titanium compound is hydrolyzed to produce hydrogen halide and titanium hydroxide by contacting the effluent containing the titanium compound with water. ..

工程(1)に係る加水分解処理において、チタン化合物を含む排液と水との混合液のpHは、0.5以上2.0以下であることが好ましく、0.7以上1.5以下であることがより好ましく、1.0程度であることがさらに好ましい。チタン化合物を含む排液と水との混合液のpHが上記範囲にあることにより、混合液中で生成した水酸化チタンが析出し難くなり、その後の処理を円滑に行うことができる。 In the hydrolysis treatment according to the step (1), the pH of the mixed solution of the effluent containing the titanium compound and water is preferably 0.5 or more and 2.0 or less, and 0.7 or more and 1.5 or less. It is more preferable that there is, and it is further preferable that it is about 1.0. When the pH of the mixture of the drainage solution containing the titanium compound and water is in the above range, the titanium hydroxide produced in the mixture is less likely to precipitate, and the subsequent treatment can be smoothly performed.

工程(1)において、チタン化合物を含む排液と接触させる水の量は、チタン化合物を含む排液1mあたり、3〜10mであることが好ましく、4〜7mであることがより好ましく、5〜6mであることがさらに好ましい。 In step (1), the amount of water contacting the waste solution containing a titanium compound, per drainage 1 m 3 containing a titanium compound is preferably 3 to 10 m 3, more preferably 4~7M 3 , 5-6 m 3 is more preferred.

工程(1)において、加水分解処理時の温度は、特に制限されないが、10〜90℃であることが好ましく、20〜70℃であることがより好ましく、30〜60℃であることがさらに好ましい。 In the step (1), the temperature during the hydrolysis treatment is not particularly limited, but is preferably 10 to 90 ° C, more preferably 20 to 70 ° C, and even more preferably 30 to 60 ° C. ..

工程(1)において、チタン化合物を含む排液と水との接触時間は、30〜60分間であることが好ましく、35〜55分間であることがより好ましく、40〜50分間であることがさらに好ましい。 In the step (1), the contact time between the drainage containing the titanium compound and water is preferably 30 to 60 minutes, more preferably 35 to 55 minutes, and further preferably 40 to 50 minutes. preferable.

本発明のチタン成分の回収方法に係る工程(2)は、工程(1)において加水分解処理を施した排液に対し、一次中和処理を施し、次いで、二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程である。 In the step (2) according to the method for recovering the titanium component of the present invention, the effluent that has been hydrolyzed in the step (1) is subjected to a primary neutralization treatment, then a secondary neutralization treatment, and then a secondary neutralization treatment. , This is a step of performing a coagulation treatment for coagulating titanium hydroxide to obtain an agglomerate of titanium hydroxide.

工程(2)では、先ず、工程(1)において加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施す。 In the step (2), first, a primary neutralization treatment in which calcium hydroxide or calcium oxide is added so that the pH of the treatment liquid subjected to the hydrolysis treatment in the step (1) is 1.5 or more and less than 2.5. To give.

一次中和処理では、工程(1)において加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように、好ましくはpHが1.8以上2.3以下となるように、より好ましくはpHが1.8以上2.2以下となるように、水酸化カルシウム又は酸化カルシウムを加える。一次中和処理時におけるpHが、上記範囲にあることにより、凝集、沈降を生じ易くなって、チタン化合物含有排液からチタン成分を高純度で回収し易くなる。一方、一次中和処理時におけるpHが1.5未満であると、円滑な中和処理を行い難くなり、また、pHが2.5以上であると、ゲル状の水酸化チタンが生成し、沈降性やろ過性が低下する。 In the primary neutralization treatment, the pH of the treatment liquid subjected to the hydrolysis treatment in step (1) is preferably 1.8 or more and 2.3 or less so that the pH is 1.5 or more and less than 2.5. Calcium hydroxide or calcium oxide is added so that the pH is more preferably 1.8 or more and 2.2 or less. When the pH at the time of the primary neutralization treatment is in the above range, aggregation and sedimentation are likely to occur, and the titanium component can be easily recovered from the titanium compound-containing effluent with high purity. On the other hand, if the pH at the time of the primary neutralization treatment is less than 1.5, it becomes difficult to perform the smooth neutralization treatment, and if the pH is 2.5 or more, gel-like titanium hydroxide is produced. Precipitability and filterability are reduced.

一次中和処理に用いられる中和剤は、水酸化カルシウム又は酸化カルシウムである。一次中和処理において、中和剤として水酸化カルシウム又は酸化カルシウムを用いることにより、中和剤コストを抑制することができ、また、中和し得られるチタン化合物の沈降性やろ過性が向上するという利点を有する。一方、一次中和処理に用いる中和剤が、例えば、水酸化ナトリウム、水酸化カリウムであると、中和剤コストが大きくなり、また、中和し得られるチタン化合物の沈降性やろ過性が悪くなり、工業的に不利となる。 The neutralizing agent used in the primary neutralization treatment is calcium hydroxide or calcium oxide. By using calcium hydroxide or calcium oxide as the neutralizing agent in the primary neutralization treatment, the cost of the neutralizing agent can be suppressed, and the sedimentability and filterability of the titanium compound obtained to be neutralized are improved. It has the advantage of. On the other hand, if the neutralizing agent used in the primary neutralization treatment is, for example, sodium hydroxide or potassium hydroxide, the cost of the neutralizing agent increases, and the neutralization and filterability of the titanium compound obtained can be improved. It gets worse and becomes industrially disadvantageous.

一次中和処理では、水酸化カルシウム又は酸化カルシウムが水に分散している懸濁液を、加水分解処理を施した処理液と接触させる。懸濁液中の水酸化カルシウム又は酸化カルシウムの含有量は、一次中和処理での水相のpHの設定値に応じて適宜選択され、好ましくは10〜300g/Lである。懸濁液中の水酸化カルシウム又は酸化カルシウムの含有量が、上記範囲にあることにより、加水分解処理を施した排液中のpHを、容易に所望範囲に制御し易い。一方、懸濁液中の水酸化カルシウムの含有量が、上記範囲を超えると加水分解処理を施した排液中のpHを制御し難くなり、また、上記範囲未満だと、円滑な中和処理を行い難くなる。 In the primary neutralization treatment, the suspension in which calcium hydroxide or calcium oxide is dispersed in water is brought into contact with the hydrolyzed treatment liquid. The content of calcium hydroxide or calcium oxide in the suspension is appropriately selected according to the pH setting value of the aqueous phase in the primary neutralization treatment, and is preferably 10 to 300 g / L. When the content of calcium hydroxide or calcium oxide in the suspension is within the above range, the pH of the hydrolyzed effluent can be easily controlled within a desired range. On the other hand, if the content of calcium hydroxide in the suspension exceeds the above range, it becomes difficult to control the pH of the hydrolyzed effluent, and if it is less than the above range, smooth neutralization treatment is performed. It becomes difficult to do.

一次中和処理時の温度は、特に制限されないが、10℃以上が好ましい。 The temperature during the primary neutralization treatment is not particularly limited, but is preferably 10 ° C. or higher.

一次中和処理において、加水分解処理を施した処理液と水酸化カルシウム又は酸化カルシウムとの接触時間は、特に制限されないが、通常、60〜120分間程度である。 In the primary neutralization treatment, the contact time between the hydrolyzed treatment liquid and calcium hydroxide or calcium oxide is not particularly limited, but is usually about 60 to 120 minutes.

工程(2)において、一次中和処理を行う方法としては、加水分解処理を施した処理液に対して、中和槽(一次中和処理槽)中で水酸化カルシウム又は酸化カルシウムを接触させて行うことが好ましく、一次中和処理槽は一槽であってもよいし、複数槽が連通したものであってもよい。 In the step (2), as a method of performing the primary neutralization treatment, calcium hydroxide or calcium oxide is brought into contact with the hydrolyzed treatment liquid in a neutralization tank (primary neutralization treatment tank). This is preferably performed, and the primary neutralization treatment tank may be one tank or a plurality of tanks in communication with each other.

工程(2)では、次いで、一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施す。 In the step (2), the treatment liquid subjected to the primary neutralization treatment is then subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added so that the pH is 6.5 or more and 7.5 or less.

工程(2)に係る二次中和処理時において、一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように水酸化カルシウム又は酸化カルシウムを加える。そして、工程(2)に係る二次中和処理時において、一次中和処理を施した処理液に対し、pHが6.5以上7.5以下となるように水酸化カルシウム又は酸化カルシウムを加えることが好ましく、pHが6.4以上7.5以下となるように水酸化カルシウム又は酸化カルシウムを加えることがより好ましく、pHが6.3以上7.5以下となるように水酸化カルシウム又は酸化カルシウムを加えることがさらに好ましい。 At the time of the secondary neutralization treatment according to the step (2), calcium hydroxide or calcium oxide is added to the treatment liquid subjected to the primary neutralization treatment so that the pH is 6.5 or more and 7.5 or less. Then, at the time of the secondary neutralization treatment according to the step (2), calcium hydroxide or calcium oxide is added to the treatment liquid subjected to the primary neutralization treatment so that the pH is 6.5 or more and 7.5 or less. It is preferable to add calcium hydroxide or calcium oxide so that the pH is 6.4 or more and 7.5 or less, and calcium hydroxide or oxidation is more preferable so that the pH is 6.3 or more and 7.5 or less. It is even more preferable to add calcium.

二次中和処理におけるpHが、上記範囲にあることにより、凝集処理を経て得られる水酸化チタンの凝集物中のカルシウム含有量が少なくなり、また、凝集、沈降を生じ易くなって、チタン化合物含有排液からチタン成分を高純度で回収し易くなる。一方、二次中和処理時におけるpHが、上記範囲未満だと、水酸化チタンが析出し難くなり、また、上記範囲を超えると、凝集処理を経て得られる水酸化チタンの凝集物中のカルシウム含有量が多くなり過ぎる。 When the pH in the secondary neutralization treatment is in the above range, the calcium content in the agglutination of titanium hydroxide obtained through the agglutination treatment is reduced, and aggregation and sedimentation are likely to occur, so that the titanium compound It becomes easy to recover the titanium component from the contained effluent with high purity. On the other hand, if the pH at the time of the secondary neutralization treatment is less than the above range, it becomes difficult for titanium hydroxide to precipitate, and if it exceeds the above range, calcium in the agglutination of titanium hydroxide obtained through the agglutination treatment The content is too high.

二次中和処理に用いられる中和剤は、水酸化カルシウム又は酸化カルシウムである。二次中和処理において、中和剤として水酸化カルシウム又は酸化カルシウムを用いることにより、中和剤コストを抑制することができ、また、中和し得られるチタン化合物の沈降性やろ過性が向上するという利点を有する。一方、二次中和処理に用いる中和剤が、例えば、水酸化ナトリウム、水酸化カリウムであると、中和剤コストが大きくなり、また、中和し得られるチタン化合物の沈降性やろ過性が悪くなり、工業的に不利となる。 The neutralizing agent used in the secondary neutralization treatment is calcium hydroxide or calcium oxide. By using calcium hydroxide or calcium oxide as the neutralizing agent in the secondary neutralization treatment, the cost of the neutralizing agent can be suppressed, and the sedimentation property and filterability of the titanium compound obtained to be neutralized are improved. Has the advantage of On the other hand, if the neutralizing agent used in the secondary neutralization treatment is, for example, sodium hydroxide or potassium hydroxide, the cost of the neutralizing agent increases, and the neutralizing property of the titanium compound and the filterability of the titanium compound can be obtained. Will be worse and industrially disadvantageous.

二次中和処理では、水酸化カルシウム又は酸化カルシウムが水に分散している懸濁液を、一次中和処理を施した処理液と接触させる。懸濁液中の水酸化カルシウム又は酸化カルシウムの含有量は、二次中和処理での水相のpHの設定値に応じて適宜選択され、好ましくは10〜300g/Lである。懸濁液中の水酸化カルシウム又は酸化カルシウムの含有量が、上記範囲にあることにより、一次中和処理を施した処理液中のpHを、容易に所望範囲に制御し易い。一方、懸濁液中の水酸化カルシウム又は酸化カルシウムの含有量が、上記範囲を超えると一次中和処理を施した処理中のpHを制御し難くなり、また、上記範囲未満だと、円滑な中和処理を行い難くなる。 In the secondary neutralization treatment, the suspension in which calcium hydroxide or calcium oxide is dispersed in water is brought into contact with the treatment liquid subjected to the primary neutralization treatment. The content of calcium hydroxide or calcium oxide in the suspension is appropriately selected according to the pH setting value of the aqueous phase in the secondary neutralization treatment, and is preferably 10 to 300 g / L. When the content of calcium hydroxide or calcium oxide in the suspension is in the above range, the pH in the treatment liquid subjected to the primary neutralization treatment can be easily controlled within a desired range. On the other hand, if the content of calcium hydroxide or calcium oxide in the suspension exceeds the above range, it becomes difficult to control the pH during the treatment subjected to the primary neutralization treatment, and if it is less than the above range, it is smooth. It becomes difficult to perform neutralization treatment.

二次中和処理時の温度は、特に制限されないが、10℃以上が好ましい。 The temperature during the secondary neutralization treatment is not particularly limited, but is preferably 10 ° C. or higher.

二次中和処理において、一次中和処理を施した処理液と水酸化カルシウム又は酸化カルシウムとの接触時間は、特に制限されないが、通常、60〜120分間程度である。 In the secondary neutralization treatment, the contact time between the treatment liquid subjected to the primary neutralization treatment and calcium hydroxide or calcium oxide is not particularly limited, but is usually about 60 to 120 minutes.

工程(2)において、二次中和処理を行う方法としては、一次中和処理を施した処理液に対して、中和槽(二次中和処理槽)中で水酸化カルシウム又は酸化カルシウムを接触させて行うことが好ましく、二次中和処理槽は一槽であってもよいし、複数槽が連通したものであってもよい。 In the step (2), as a method of performing the secondary neutralization treatment, calcium hydroxide or calcium oxide is added to the treatment liquid subjected to the primary neutralization treatment in a neutralization tank (secondary neutralization treatment tank). It is preferable to carry out the process in contact with each other, and the secondary neutralization treatment tank may be one tank or a plurality of tanks in communication with each other.

また、二次中和処理後の処理液中には、水酸化カルシウムが含有されていなことが好ましい。なお、二次中和処理後の処理液中の水酸化カルシウム含有量は、二次中和処理において添加する中和剤の量、二次中和処理でのpHの設定値等により、調節される。 Further, it is preferable that the treatment liquid after the secondary neutralization treatment does not contain calcium hydroxide. The calcium hydroxide content in the treatment liquid after the secondary neutralization treatment is adjusted by the amount of the neutralizing agent added in the secondary neutralization treatment, the pH setting value in the secondary neutralization treatment, and the like. NS.

工程(2)においては、次いで、二次中和処理を施した処理液中の水酸化チタンを凝集させる凝集処理を施す。凝集処理には、アニオン系高分子凝集剤などの凝集剤を用いて行う化学的処理を適用してもよいし、フィルタープレス、液体サイクロン、遠心分離などの各種装置を用いた機械的処理(脱水処理)を適用してもよい。廃液の成分や濃度などに応じて、凝集処理の方法を適宜選択すればよい。凝集処理を施すことで、後工程における濾過処理の時間を短縮することができる。 In the step (2), an agglutination treatment for agglutinating titanium hydroxide in the treatment liquid subjected to the secondary neutralization treatment is then performed. For the coagulation treatment, a chemical treatment performed using a coagulant such as an anionic polymer coagulant may be applied, or a mechanical treatment (dehydration) using various devices such as a filter press, a liquid cyclone, and a centrifuge may be applied. Processing) may be applied. The method of coagulation treatment may be appropriately selected according to the components and concentration of the waste liquid. By performing the coagulation treatment, the time of the filtration treatment in the subsequent process can be shortened.

工程(2)において、水酸化チタンの凝集は、二次中和処理を施した処理液を凝集槽中に送入して同槽内で行うことが好ましい。そして、凝集処理を行うことにより、水酸化チタンの凝集物が生じる。 In the step (2), it is preferable that the agglutination of titanium hydroxide is carried out in the agglutination tank by feeding the treatment liquid subjected to the secondary neutralization treatment into the agglutination tank. Then, by performing the agglutination treatment, agglomerates of titanium hydroxide are generated.

工程(2)では、水酸化チタンを凝集させることにより、水酸化チタンの凝集物が生じるが、工程(2)を行った後は、生じた水酸化チタンの凝集物を含む凝集処理液から、液相の一部又は全部を分離してから、後段の工程を行ってもよいし、あるいは、生じた水酸化チタンの凝集物を含む凝集処理液からの液相の分離を行わずに、後段の工程を行ってもよい。 In step (2), agglomerates of titanium hydroxide are generated by aggregating titanium hydroxide, but after performing step (2), a coagulation treatment liquid containing the generated agglomerates of titanium hydroxide is used. After separating a part or all of the liquid phase, the subsequent step may be performed, or the latter stage may be performed without separating the liquid phase from the coagulation treatment liquid containing the generated agglomerates of titanium hydroxide. You may perform the process of.

工程(2)又は工程(2)より後段の工程において、水酸化チタンの凝集物を含む凝集処理液から分離した水相については、酸性度を中性(pH6.5〜7.5)に調整した上で、適宜、廃液処理することが好ましい。 In the step (2) or the step after the step (2), the acidity of the aqueous phase separated from the agglutination treatment liquid containing the agglutination of titanium hydroxide is adjusted to neutral (pH 6.5 to 7.5). After that, it is preferable to treat the waste liquid as appropriate.

例えば、本発明のチタン成分の回収方法では、工程(2)を行った後、生じた水酸化チタンの凝集物を、沈降槽内で沈降させて、沈降槽内の水酸化チタンの凝集物の沈降物を抜き出すことにより、水酸化チタンの凝集物を、水酸化チタンの凝集物の沈降物の状態で分離する。この水酸化チタンの凝集物の沈降物は、それまでの処理に由来する液相を含んでいるが、工程(2)より後段で行う酸処理には、水酸化チタンの凝集物の沈降物中の液相を除去してから供してもよいし、あるいは、水酸化チタンの凝集物の沈降物中の液相を除去せずに供してもよい。 For example, in the method for recovering the titanium component of the present invention, after performing step (2), the generated titanium hydroxide agglomerates are settled in the settling tank, and the titanium hydroxide agglomerates in the settling tank are settled. By extracting the precipitate, the agglomerates of titanium hydroxide are separated in the state of the agglomerates of titanium hydroxide. The precipitate of the agglomerates of titanium hydroxide contains a liquid phase derived from the treatment up to that point, but in the acid treatment performed after the step (2), the precipitate of the agglomerates of titanium hydroxide is contained. The liquid phase may be provided after removing the liquid phase of the above, or the liquid phase in the precipitate of the aggregate of titanium hydroxide may be provided without being removed.

本発明のチタン成分の回収方法では、工程(2)より後段の処理工程において、水酸化チタンの凝集物に塩酸を接触させる酸処理を施す。本発明のチタン成分の回収方法において、酸処理を施す時期は、工程(2)より後段であれば、特に制限されない。そして、本発明のチタン成分の回収方法では、水酸化チタンの凝集物に塩酸を接触させることにより、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。 In the method for recovering the titanium component of the present invention, in the treatment step after the step (2), an acid treatment is performed in which the agglomerates of titanium hydroxide are brought into contact with hydrochloric acid. In the method for recovering the titanium component of the present invention, the time for applying the acid treatment is not particularly limited as long as it is after the step (2). Then, in the method for recovering the titanium component of the present invention, the calcium content in the titanium hydroxide agglutination can be reduced by bringing hydrochloric acid into contact with the titanium hydroxide agglutination.

本発明のチタン成分の回収方法に係る酸処理では、工程(2)を行い得られる水酸化チタンの凝集物に、塩酸を接触させるが、このとき、液相のpHが5.9以下となるように塩酸を接触させる。酸処理時の液相のpHが、上記範囲にあることにより、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。一方、酸処理時の液相のpHが上記範囲を超えると、水酸化チタンの凝集物中のカルシウム含有量を少なくする効果が得られ難くなる。酸処理時の液相のpHの上限については、好ましくは5.7以下、より好ましくは以下5.5以下、更に好ましくは5.3以下である。また、酸処理時の液相のpHの下限については、好ましくは2.0以上、より好ましくは3.0以上である。 In the acid treatment according to the method for recovering the titanium component of the present invention, hydrochloric acid is brought into contact with the aggregate of titanium hydroxide obtained in step (2), but at this time, the pH of the liquid phase becomes 5.9 or less. Bring the hydrochloric acid into contact. When the pH of the liquid phase during the acid treatment is in the above range, the calcium content in the titanium hydroxide agglutination can be reduced. On the other hand, if the pH of the liquid phase during the acid treatment exceeds the above range, it becomes difficult to obtain the effect of reducing the calcium content in the aggregate of titanium hydroxide. The upper limit of the pH of the liquid phase during the acid treatment is preferably 5.7 or less, more preferably 5.5 or less, still more preferably 5.3 or less. The lower limit of the pH of the liquid phase during the acid treatment is preferably 2.0 or more, more preferably 3.0 or more.

酸処理に用いられる酸は、塩酸である。塩化水素は、酸処理を行った後の水酸化チタンの凝集物の乾燥又は酸化の際に、生成物中から揮発して、除去されるので、酸処理に用いた塩酸に由来する塩素分が、生成物中に残留し難い。 The acid used for acid treatment is hydrochloric acid. Hydrogen chloride is volatilized and removed from the product when the agglomerates of titanium hydroxide are dried or oxidized after the acid treatment, so that the chlorine content derived from the hydrochloric acid used in the acid treatment is removed. , Hard to remain in the product.

酸処理に用いる塩酸の濃度は、特に制限されないが、1.0〜8.5mol/Lであることが好ましく、1.5〜7.0mol/Lであることが好ましく、2.7〜5.5mol/Lであることがより好ましい。酸処理に用いる塩酸の濃度が、上記範囲にあることにより、酸処理時の液相のpHを、容易に所望範囲に制御することができる。酸処理に用いる塩酸の濃度が、上記範囲を超えると酸処理時の液相のpHを制御し難くなり、また、上記範囲未満だと、円滑な酸処理を行い難くなる。 The concentration of hydrochloric acid used for the acid treatment is not particularly limited, but is preferably 1.0 to 8.5 mol / L, preferably 1.5 to 7.0 mol / L, and 2.7 to 5.5. It is more preferably 5 mol / L. When the concentration of hydrochloric acid used for the acid treatment is within the above range, the pH of the liquid phase during the acid treatment can be easily controlled within a desired range. If the concentration of hydrochloric acid used for the acid treatment exceeds the above range, it becomes difficult to control the pH of the liquid phase during the acid treatment, and if it is less than the above range, it becomes difficult to perform a smooth acid treatment.

酸処理時の温度は、特に制限されないが、10〜50℃であることが好ましく、15〜45℃であることがより好ましく、20〜40℃であることがさらに好ましい。 The temperature during the acid treatment is not particularly limited, but is preferably 10 to 50 ° C, more preferably 15 to 45 ° C, and even more preferably 20 to 40 ° C.

酸処理において、工程(2)を行い得られる水酸化チタンの凝集物と塩酸との接触時間は、60〜120分間であることが好ましく、60〜100分間であることがより好ましく、60〜80分間であることがさらに好ましい。 In the acid treatment, the contact time between the agglutinated titanium hydroxide obtained by performing the step (2) and hydrochloric acid is preferably 60 to 120 minutes, more preferably 60 to 100 minutes, and 60 to 80 minutes. Minutes are even more preferred.

本発明のチタン成分の回収方法において、酸処理を行い生成する水酸化チタンは、Ti(OH)である。つまり、本発明のチタン成分の回収方法では、水酸化チタンの凝集物の状態で、チタン化合物を含む排液からチタン成分が回収される。そして、回収された水酸化チタンの凝集物(酸処理物)は、乾燥及び酸化後、酸化チタンに変換されて、種々のチタン化合物の製造原料として用いられる。 In the method for recovering the titanium component of the present invention, the titanium hydroxide produced by acid treatment is Ti (OH) 4 . That is, in the method for recovering the titanium component of the present invention, the titanium component is recovered from the effluent containing the titanium compound in the state of agglomerates of titanium hydroxide. Then, the recovered agglomerates of titanium hydroxide (acid-treated product) are converted into titanium oxide after drying and oxidation, and used as a raw material for producing various titanium compounds.

本発明のチタン成分の回収方法においては、チタン化合物を含む排水に対し、加水分解処理後、水酸化カルシウムを中和剤として用いて、特定のpHで一次中和処理及び二次中和処理、凝集処理を順次施し、得られる水酸化チタンの凝集物に、塩酸を接触させる酸処理を施すことにより、酸処理を行い得られる水酸化チタンの凝集物中のカルシウム含有量を少なくすることができることから、カルシウム含有量が少ない水酸化チタンを高い収率で回収することができる。本発明のチタン成分の回収方法では、水酸化チタンの凝集物の酸処理を行うことにより、該水酸化チタンの凝集物に残存する水酸化カルシウム等の難水溶性未反応物質を溶解除去するので、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。以上のことから、本発明のチタン成分の回収方法では、カルシウム含有量が少ない水酸化チタンを回収し得ると考えられる。 In the method for recovering a titanium component of the present invention, wastewater containing a titanium compound is hydrolyzed, and then calcium hydroxide is used as a neutralizing agent to perform a primary neutralization treatment and a secondary neutralization treatment at a specific pH. By sequentially performing the agglomeration treatment and subjecting the obtained agglomerates of titanium hydroxide to an acid treatment in which hydrochloric acid is brought into contact, the calcium content in the agglomerates of titanium hydroxide obtained by the acid treatment can be reduced. Therefore, titanium hydroxide having a low calcium content can be recovered in a high yield. In the method for recovering the titanium component of the present invention, the poorly water-soluble unreacted substance such as calcium hydroxide remaining in the titanium hydroxide agglomerates is dissolved and removed by acid treatment of the titanium hydroxide agglomerates. , The calcium content in the agglomerates of titanium hydroxide can be reduced. From the above, it is considered that titanium hydroxide having a low calcium content can be recovered by the method for recovering the titanium component of the present invention.

本発明のチタン成分の回収方法において、酸処理を行う方法は、特に制限されず、適宜選択され、酸処理を行う時期は、工程(2)より後段であれば、いずれの時期であってよく、また、酸処理を行う方法は、水酸化チタンの凝集物と塩酸を接触させるものであれば、如何なる方法であってもよい。本発明のチタン成分の回収方法としては、以下に示す形態が挙げられる。 In the method for recovering the titanium component of the present invention, the method for performing the acid treatment is not particularly limited and may be appropriately selected, and the time for performing the acid treatment may be any time as long as it is later than the step (2). Further, the method for performing the acid treatment may be any method as long as the aggregate of titanium hydroxide is brought into contact with hydrochloric acid. Examples of the method for recovering the titanium component of the present invention include the following forms.

本発明の第一の形態のチタン成分の回収方法は、工程(2)を行い生じる水酸化チタンの凝集物の濃縮物を得た後、水酸化チタンの凝集物の濃縮物を分離し、次いで、水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3A)を有する形態である。 In the method for recovering the titanium component according to the first aspect of the present invention, the step (2) is carried out to obtain a concentrated titanium hydroxide agglomerate, and then the concentrated titanium hydroxide agglomerate is separated and then. In the form of having a step (3A) of contacting the concentrate of the titanium hydroxide agglomerate with hydrochloric acid to perform acid treatment of the titanium hydroxide agglomerate to obtain an acid-treated product of the titanium hydroxide agglomerate. be.

すなわち、本発明の第一の形態のチタン成分の回収方法は、チタン化合物を含む排液からチタン成分を回収するチタン成分の回収方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理水に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)を行い生じる該水酸化チタンの凝集物の濃縮物を得た後、水酸化チタンの凝集物の濃縮物を分離し、次いで、該水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3A)と、
を有すること、
を特徴とするチタン成分の回収方法である。本発明の第一の形態のチタン成分の回収方法は、工程(2)において水酸化チタンの凝集物を生じさせた後、凝集処理液から水酸化チタンの凝集物の濃縮物を分離し、水酸化チタンの凝集物の濃縮物に対し、酸処理を施す形態である。
That is, the method for recovering the titanium component according to the first aspect of the present invention is a method for recovering the titanium component from the effluent containing the titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treated water is subjected to a primary neutralization treatment in which calcium hydroxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization treatment is performed. The treated liquid was subjected to a secondary neutralization treatment in which calcium hydroxide was added as a neutralizing agent so that the pH was 6.5 or more and 7.5 or less, and then a coagulation treatment for aggregating titanium hydroxide was performed. Step (2) to obtain agglomerates of titanium hydroxide,
After the step (2) is performed to obtain a concentrate of the titanium hydroxide agglomerate, the titanium hydroxide agglomerate concentrate is separated, and then the titanium hydroxide agglomerate concentrate is added to the concentrate. The step (3A) of contacting with hydrochloric acid to perform acid treatment of the titanium hydroxide agglomerate to obtain an acid-treated product of the titanium hydroxide agglomerate.
To have
It is a method for recovering a titanium component, which is characterized by the above. In the method for recovering the titanium component according to the first aspect of the present invention, after forming a titanium hydroxide agglomerate in the step (2), the titanium hydroxide agglomerate concentrate is separated from the agglomeration treatment liquid, and water is used. This is a form in which an acid treatment is applied to a concentrate of titanium oxide aggregates.

本発明の第一の形態のチタン成分の回収方法について、図2を参照して説明する。図2は、本発明の第一の形態のチタン成分の回収方法の形態例のフロー図である。なお、ここでも中和剤として水酸化カルシウムを適用した形態を例に挙げて説明するが、本発明においては、中和剤として酸化カルシウムを適用しても、水酸化カルシウムを適用した場合と同様の効果が得られる。図2中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物を生じさせる。次いで、生じた水酸化チタンの凝集物を含む凝集処理液を、沈降槽5に移送し、沈降槽5内で、水酸化チタンの凝集物を沈降させて、沈降槽5の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出す。次いで、沈降槽5から抜き出した水酸化チタンの凝集物の沈降物を、沈降物貯蔵槽6に移送する。次いで、水酸化チタンの凝集物の沈降物を、フィルタープレス装置7を用いてろ過し、水酸化チタンの凝集物の沈降物から液相を除去して、水酸化チタンの凝集物をろ別し、水酸化チタンの凝集物のプレスケーキを得る。次いで、水酸化チタンの凝集物のプレスケーキを、酸処理槽8に移送し、酸処理槽8に塩酸14を供給して、水酸化チタンの凝集物と塩酸14を混合し、酸処理を施す。次いで、水酸化チタンの凝集物の酸処理物を、フィルタープレス装置9を用いてろ過し、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別し、水酸化チタンの凝集物の酸処理物のプレスケーキ21を得る。 The method for recovering the titanium component according to the first aspect of the present invention will be described with reference to FIG. FIG. 2 is a flow chart of an example of a method for recovering a titanium component according to the first aspect of the present invention. Although a form in which calcium hydroxide is applied as a neutralizing agent will be described here as an example, in the present invention, even if calcium oxide is applied as a neutralizing agent, it is the same as when calcium hydroxide is applied. The effect of is obtained. In FIG. 2, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and titanium hydroxide is agglomerated to generate agglomerates of titanium hydroxide. Let me. Next, the agglutination treatment liquid containing the generated titanium hydroxide agglomerates is transferred to the settling tank 5, and the titanium hydroxide agglomerates are settled in the settling tank 5 from the lower part or the bottom of the settling tank 5. Extract the sediment of titanium hydroxide agglomerates. Next, the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank 5 is transferred to the sediment storage tank 6. Next, the precipitate of the titanium hydroxide agglomerate is filtered using the filter press device 7, the liquid phase is removed from the precipitate of the titanium hydroxide agglomerate, and the titanium hydroxide agglomerate is filtered out. , Obtain a press cake of agglomerates of titanium hydroxide. Next, the press cake of the agglutinated titanium hydroxide is transferred to the acid treatment tank 8, the hydrochloric acid 14 is supplied to the acid treatment tank 8, the agglutinate of titanium hydroxide and the hydrochloric acid 14 are mixed, and the acid treatment is performed. .. Next, the acid-treated product of the titanium hydroxide aggregate is filtered using the filter press device 9, the liquid phase is removed from the acid-treated product of the titanium hydroxide aggregate, and the acid of the titanium hydroxide aggregate is removed. The treated product is filtered off to obtain a press cake 21 of an acid-treated product of agglomerates of titanium hydroxide.

本発明の第一の形態のチタン成分の回収方法は、工程(1)、工程(2)と、工程(3A)と、を有する。本発明の第一の形態のチタン成分の回収方法における工程(1)、工程(2)、用いる排水、処理及び処理方法等については、本発明のチタン化合物の回収方法と共通し、その詳細については、本発明のチタン成分の回収方法の説明で述べた通りである。 The method for recovering the titanium component according to the first aspect of the present invention includes steps (1), steps (2), and steps (3A). The steps (1), steps (2), wastewater used, treatment, treatment method, etc. in the titanium component recovery method of the first aspect of the present invention are common to the titanium compound recovery method of the present invention, and details thereof. Is as described in the description of the method for recovering the titanium component of the present invention.

本発明の第一の形態のチタン成分の回収方法に係る工程(3A)では、工程(2)を行い生じる水酸化チタンの凝集物の濃縮物を得た後、得られた水酸化チタンの凝集物の濃縮物を、凝集処理液から分離する。 In the step (3A) according to the method for recovering the titanium component of the first aspect of the present invention, after the concentrate of the titanium hydroxide agglomerate produced by performing the step (2) is obtained, the obtained agglomeration of titanium hydroxide is obtained. The concentrate of the product is separated from the coagulation treatment liquid.

工程(3A)において、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液から、水酸化チタンの凝集物の濃縮物を得る方法としては、特に制限されない。例えば、先ず、(i)工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液を、沈降槽に移送し、沈降槽内で、水酸化チタンの凝集物を沈降させる。次いで、(ii)沈降槽の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出して、凝集処理液から水酸化チタンの凝集物の沈降物を分離し、沈降槽から抜き出した水酸化チタンの凝集物の沈降物を、沈降物貯蔵槽に移送して、水酸化チタンの凝集物の沈降物、すなわち、水酸化チタンの凝集物の濃縮物を得る。 In the step (3A), the method for obtaining the concentrate of the titanium hydroxide agglutination from the agglutination treatment liquid containing the titanium hydroxide agglutination after the step (2) is not particularly limited. For example, first, the agglutination treatment liquid containing the titanium hydroxide agglomerates after the step (i) (2) is transferred to a settling tank, and the titanium hydroxide agglomerates are settled in the settling tank. Next, (ii) the sediment of the titanium hydroxide agglomerate was extracted from the lower part or the bottom of the settling tank, the sediment of the titanium hydroxide agglomerate was separated from the coagulation treatment liquid, and the hydroxylation extracted from the settling tank. The sediment of titanium agglomerates is transferred to a sediment storage tank to obtain a precipitate of titanium hydroxide agglomerates, that is, a concentrate of titanium hydroxide agglomerates.

また、工程(3A)において、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液から、水酸化チタンの凝集物の濃縮物を得る方法としては、他には、例えば、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液を、液体サイクロン、スクリューデカンタ等で処理して、凝集処理液から水相を分離し、水酸化チタンの凝集物の濃縮物を得る方法が挙げられる。 Further, in the step (3A), as a method for obtaining a concentrate of the agglomerates of titanium hydroxide from the agglutination treatment liquid containing the agglutinates of titanium hydroxide after the step (2), for example, , The agglutination treatment liquid containing the agglutination of titanium hydroxide after the step (2) is treated with a liquid cyclone, a screw decanter, etc. to separate the aqueous phase from the agglutination treatment liquid, and the agglutination of titanium hydroxide. There is a method of obtaining the concentrate of.

また、工程(3A)において、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液から、水酸化チタンの凝集物の濃縮物を得る方法としては、先ず、工程(2)を行い生じる水酸化チタンの凝集物を沈降させた後、凝集処理液から、水酸化チタンの凝集物の沈降物を分離し、次いで、水酸化チタンの凝集物の沈降物から液相を除去する脱水処理を行い、水酸化チタンの凝集物の脱水処理物を得ることにより、水酸化チタンの凝集物の脱水処理物、すなわち、水酸化チタンの凝集物の濃縮物を得る方法が挙げられる。脱水処理方法としては、例えば、フィルタープレス装置、遠心分離装置、液体サイクロン装置等の固液分離装置を用いて、ろ過する方法が挙げられる。 Further, in the step (3A), as a method of obtaining a concentrate of the agglomerates of titanium hydroxide from the coagulation treatment liquid containing the agglomerates of titanium hydroxide after the step (2), first, the step (2). ) To settle the resulting agglomerates of titanium hydroxide, separate the settling of the agglomerates of titanium hydroxide from the agglomeration treatment liquid, and then remove the liquid phase from the settling of the agglomerates of titanium hydroxide. A method of obtaining a dehydrated product of titanium hydroxide agglomerates, that is, a concentrate of titanium hydroxide agglomerates by performing a dehydration treatment for obtaining a dehydrated product of titanium hydroxide agglomerates can be mentioned. Examples of the dehydration treatment method include a method of filtering using a solid-liquid separator such as a filter press device, a centrifuge device, and a liquid cyclone device.

工程(3A)では、次いで、水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、水酸化チタンの凝集物の酸処理を行う。 In the step (3A), hydrochloric acid is then brought into contact with the concentrate of the titanium hydroxide agglutination to perform acid treatment of the titanium hydroxide agglutination.

工程(3A)に係る酸処理では、水酸化チタンの凝集物の脱水処理物に、塩酸を接触させるが、このとき、液相のpHが5.9以下、好ましくは2.0以上5.5以下、より好ましくは3.5以上5.0以下となるように塩酸を接触させる。酸処理時の液相のpHが、上記範囲にあることにより、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。一方、酸処理時の液相のpHが5.9を超えると、水酸化チタンの凝集物中のカルシウム含有量を少なくする効果が得られ難くなる。 In the acid treatment according to the step (3A), hydrochloric acid is brought into contact with the dehydrated product of the agglomerates of titanium hydroxide. At this time, the pH of the liquid phase is 5.9 or less, preferably 2.0 or more and 5.5. Hereinafter, hydrochloric acid is contacted so as to be more preferably 3.5 or more and 5.0 or less. When the pH of the liquid phase during the acid treatment is in the above range, the calcium content in the titanium hydroxide agglutination can be reduced. On the other hand, if the pH of the liquid phase during the acid treatment exceeds 5.9, it becomes difficult to obtain the effect of reducing the calcium content in the aggregate of titanium hydroxide.

工程(3A)に係る酸処理に用いられる酸は、塩酸である。塩化水素は、酸処理を行った後の水酸化チタンの凝集物の乾燥又は酸化の際に、生成物中から揮発して、除去されるので、塩酸に由来する塩素分が、生成物中に残留し難い。 The acid used for the acid treatment according to the step (3A) is hydrochloric acid. Hydrogen chloride is volatilized and removed from the product when the agglutinate of titanium hydroxide is dried or oxidized after the acid treatment, so that chlorine derived from hydrochloric acid is contained in the product. Hard to remain.

工程(3A)に係る酸処理に用いる塩酸の濃度は、特に制限されないが1.0〜8.5mol/Lであることが好ましく、1.5〜7.0mol/Lであることが好ましく、2.7〜5.5mol/Lであることがより好ましい。酸処理に用いる塩酸の濃度が、上記範囲にあることにより、酸処理時の液相のpHを、容易に所望範囲に制御することができる。酸処理に用いる塩酸の濃度が、上記範囲を超えると酸処理時の液相のpHを制御し難くなり、また、上記範囲未満だと、円滑な酸処理を行い難くなる。 The concentration of hydrochloric acid used for the acid treatment according to the step (3A) is not particularly limited, but is preferably 1.0 to 8.5 mol / L, preferably 1.5 to 7.0 mol / L, and 2 It is more preferably .7 to 5.5 mol / L. When the concentration of hydrochloric acid used for the acid treatment is within the above range, the pH of the liquid phase during the acid treatment can be easily controlled within a desired range. If the concentration of hydrochloric acid used for the acid treatment exceeds the above range, it becomes difficult to control the pH of the liquid phase during the acid treatment, and if it is less than the above range, it becomes difficult to perform a smooth acid treatment.

工程(3A)に係る酸処理時の温度は、特に制限されないが、10〜50℃であることが好ましく、15〜45℃であることがより好ましく、20〜40℃であることがさらに好ましい。 The temperature during the acid treatment according to the step (3A) is not particularly limited, but is preferably 10 to 50 ° C, more preferably 15 to 45 ° C, and even more preferably 20 to 40 ° C.

工程(3A)に係る酸処理において、水酸化チタンの凝集物の脱水処理物と塩酸との接触時間は、60〜120分間であることが好ましく、60〜100分間であることがより好ましく、60〜80分間であることがさらに好ましい。 In the acid treatment according to the step (3A), the contact time between the dehydrated product of the titanium hydroxide aggregate and hydrochloric acid is preferably 60 to 120 minutes, more preferably 60 to 100 minutes, and 60. It is more preferably ~ 80 minutes.

工程(3A)において、酸処理を行う方法としては、水酸化チタンの凝集物の脱水処理物に対して、酸処理槽中で塩酸を接触させて行うことが好ましい。 In the step (3A), as a method of performing the acid treatment, it is preferable to bring the dehydrated product of the titanium hydroxide agglutinate into contact with hydrochloric acid in the acid treatment tank.

工程(3A)において、酸処理を行った後は、固液分離装置を用いて、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物の脱水処理物を得、更に、脱水処理物を60〜200℃で乾燥して、水酸化チタンの凝集物の酸処理物を得る。この水酸化チタンの凝集物の酸処理物からの液相の除去及び乾燥により、水酸化チタンの凝集物の酸処理物から水及び塩化水素が除去され、水酸化チタンの凝集物の酸処理物が得られる。 In the step (3A), after the acid treatment, the liquid phase is removed from the acid-treated product of the titanium hydroxide agglomerate using a solid-liquid separator, and the acid-treated product of the titanium hydroxide agglomerate is removed. The dehydrated product of No. 1 is obtained, and the dehydrated product is further dried at 60 to 200 ° C. to obtain an acid-treated product of agglomerates of titanium hydroxide. By removing the liquid phase from the acid-treated product of the titanium hydroxide agglomerates and drying, water and hydrogen chloride are removed from the acid-treated product of the titanium hydroxide agglomerates, and the acid-treated product of the titanium hydroxide agglomerates. Is obtained.

本発明の第一の形態のチタン成分の回収方法において、工程(3A)を行い得られる水酸化チタンは、Ti(OH)である。つまり、本発明のチタン成分の回収方法では、水酸化チタンの凝集物の状態で、チタン化合物を含む排液からチタン成分が回収される。そして、回収された水酸化チタンの凝集物(酸処理物)は、乾燥及び酸化後、酸化チタンに変換されて、種々のチタン化合物の製造原料として用いられる。 In the method for recovering the titanium component of the first aspect of the present invention, the titanium hydroxide obtained by performing the step (3A) is Ti (OH) 4 . That is, in the method for recovering the titanium component of the present invention, the titanium component is recovered from the effluent containing the titanium compound in the state of agglomerates of titanium hydroxide. Then, the recovered agglomerates of titanium hydroxide (acid-treated product) are converted into titanium oxide after drying and oxidation, and used as a raw material for producing various titanium compounds.

本発明の第一の形態のチタン成分の回収方法においては、チタン化合物を含む排水に対し、加水分解処理後、水酸化カルシウム又は酸化カルシウムを中和剤として用いて、特定のpHで一次中和処理及び二次中和処理、凝集処理を順次施し、水酸化チタンの凝集物を生じさせ、次いで、水相を分離して、得られる水酸化チタンの凝集物の濃縮物に対し、塩酸を接触させる酸処理を施すことにより、酸処理を行い得られる水酸化チタンの凝集物中のカルシウム含有量を少なくすることができることから、カルシウム含有量が少ない水酸化チタンを回収することができる。本発明の第一の形態のチタン成分の回収方法では、工程(2)で生じた水酸化チタンの凝集物の濃縮物に対し酸処理を行うことで、水酸化チタンの凝集物の酸処理を行うことにより、該水酸化チタンの凝集物に残存する水酸化カルシウム等の難水溶性未反応物質を溶解するので、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。以上のことから、本発明の第一の形態のチタン成分の回収方法では、カルシウム含有量が少ない水酸化チタンを回収し得ると考えられる。 In the method for recovering a titanium component according to the first aspect of the present invention, wastewater containing a titanium compound is first neutralized at a specific pH by using calcium hydroxide or calcium oxide as a neutralizing agent after a hydrolysis treatment. The treatment, the secondary neutralization treatment, and the agglomeration treatment are sequentially performed to form an agglomerate of titanium hydroxide, then the aqueous phase is separated, and the obtained concentrate of the agglomerate of titanium hydroxide is brought into contact with calcium. By subjecting the acid treatment to the acid treatment, the calcium content in the aggregate of titanium hydroxide obtained by the acid treatment can be reduced, so that the titanium hydroxide having a low calcium content can be recovered. In the method for recovering the titanium component according to the first aspect of the present invention, the concentrate of the titanium hydroxide agglomerate produced in the step (2) is treated with an acid to treat the titanium hydroxide agglomerate with an acid. By doing so, the poorly water-soluble unreacted substance such as calcium hydroxide remaining in the titanium hydroxide agglomerates is dissolved, so that the calcium content in the titanium hydroxide agglomerates can be reduced. From the above, it is considered that titanium hydroxide having a low calcium content can be recovered by the method for recovering the titanium component according to the first aspect of the present invention.

本発明の第一の形態のチタン成分の回収方法は、工程(1)、工程(2)及び工程(3A)に加え、工程(3A)を行い得られる水酸化チタンの凝集物の酸処理物を、pH6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することができる。洗浄工程では、工程(3A)を行い得られる水酸化チタンの凝集物の酸処理物に洗浄水を接触させることにより、洗浄を行うが、水酸化チタンの凝集物の酸処理物と洗浄水の接触方法は、特に制限されず、例えば、以下の方法が挙げられる。 The method for recovering the titanium component according to the first aspect of the present invention is an acid-treated product of a titanium hydroxide agglomerate obtained by performing step (3A) in addition to step (1), step (2) and step (3A). Can have a washing step of washing with washing water having a pH of 6.0 or more and 9.0 or less. In the cleaning step, cleaning is performed by bringing the cleaning water into contact with the acid-treated product of the titanium hydroxide agglomerates obtained in the step (3A). The contact method is not particularly limited, and examples thereof include the following methods.

図3は、本発明の第一の形態のチタン成分の回収方法のうち、洗浄工程を行う形態の形態例を示すフロー図である。なお、ここでも中和剤として水酸化カルシウムを適用した形態を例に挙げて説明するが、本発明においては、中和剤として酸化カルシウムを適用しても、水酸化カルシウムを適用した場合と同様の効果が得られる。図3中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物を生じさせる。次いで、生じた水酸化チタンの凝集物を含む凝集処理液を、沈降槽5に移送し、沈降槽5内で、水酸化チタンの凝集物を沈降させて、沈降槽5の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出す。次いで、沈降槽5から抜き出した水酸化チタンの凝集物の沈降物を、沈降物貯蔵槽6に移送する。次いで、水酸化チタンの凝集物の沈降物を、フィルタープレス装置7を用いてろ過し、水酸化チタンの凝集物の沈降物から液相を除去して、水酸化チタンの凝集物をろ別し、水酸化チタンの凝集物のプレスケーキを得る。次いで、水酸化チタンの凝集物のプレスケーキを、酸処理槽8に移送し、酸処理槽8に塩酸14を供給して、水酸化チタンの凝集物と塩酸14を混合し、酸処理を施す。次いで、水酸化チタンの凝集物の酸処理物を、フィルタープレス装置9を用いてろ過し、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別することにより、水酸化チタンの凝集物の酸処理物のプレスケーキを得る。次いで、水酸化チタンの凝集物の酸処理物のプレスケーキを、洗浄槽31に移送し、洗浄槽槽31に洗浄水15を供給して、水酸化チタンの凝集物の酸処理物と洗浄水15を混合し、洗浄を行う。次いで、水酸化チタンの凝集物の酸処理物の洗浄物を、フィルタープレス装置33を用いてろ過し、水酸化チタンの凝集物の酸処理物の洗浄物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別することにより、水酸化チタンの凝集物の酸処理物のプレスケーキ22を得る。 FIG. 3 is a flow chart showing an example of a form in which a cleaning step is performed among the methods for recovering a titanium component according to the first aspect of the present invention. Although a form in which calcium hydroxide is applied as a neutralizing agent will be described here as an example, in the present invention, even if calcium oxide is applied as a neutralizing agent, it is the same as when calcium hydroxide is applied. The effect of is obtained. In FIG. 3, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and titanium hydroxide is agglomerated to generate agglomerates of titanium hydroxide. Let me. Next, the agglutination treatment liquid containing the generated titanium hydroxide agglomerates is transferred to the settling tank 5, and the titanium hydroxide agglomerates are settled in the settling tank 5 from the lower part or the bottom of the settling tank 5. Extract the sediment of titanium hydroxide agglomerates. Next, the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank 5 is transferred to the sediment storage tank 6. Next, the precipitate of the titanium hydroxide agglomerate is filtered using the filter press device 7, the liquid phase is removed from the precipitate of the titanium hydroxide agglomerate, and the titanium hydroxide agglomerate is filtered out. , Obtain a press cake of agglomerates of titanium hydroxide. Next, the press cake of the agglutinated titanium hydroxide is transferred to the acid treatment tank 8, the hydrochloric acid 14 is supplied to the acid treatment tank 8, the agglutinate of titanium hydroxide and the hydrochloric acid 14 are mixed, and the acid treatment is performed. .. Next, the acid-treated product of the titanium hydroxide aggregate is filtered using the filter press device 9, the liquid phase is removed from the acid-treated product of the titanium hydroxide aggregate, and the acid of the titanium hydroxide aggregate is removed. By filtering the treated product, a press cake of an acid-treated product of agglomerates of titanium hydroxide is obtained. Next, the press cake of the acid-treated product of the titanium hydroxide agglomerates is transferred to the washing tank 31, and the washing water 15 is supplied to the washing tank tank 31, and the acid-treated product and the washing water of the titanium hydroxide agglomerates are supplied. 15 is mixed and washed. Next, the washed product of the acid-treated product of the agglomerates of titanium hydroxide is filtered using the filter press device 33, the liquid phase is removed from the washed product of the acid-treated product of the aggregates of titanium hydroxide, and hydroxylation is performed. By filtering the acid-treated product of the titanium agglomerates, a press cake 22 of the acid-treated product of the titanium hydroxide agglomerates is obtained.

つまり、洗浄工程の第一の形態は、工程(3A)を行い得られる水酸化チタンの凝集物の酸処理物を、フィルタープレス装置、遠心分離装置、液体サイクロン装置等の固液分離装置を用いて、水酸化チタンの凝集物の酸処理物を液相と分離し、プレスケーキ等の脱水処理物を得、次いで、プレスケーキ等の脱水処理物を、固液分離装置から取り出し、次いで、脱水処理物に洗浄水を接触させることにより、洗浄を行う形態である。 That is, in the first form of the cleaning step, the acid-treated product of the aggregate of titanium hydroxide obtained by performing the step (3A) is subjected to a solid-liquid separation device such as a filter press device, a centrifugation device, and a liquid cyclone device. The acid-treated product of the aggregate of titanium hydroxide is separated from the liquid phase to obtain a dehydrated product such as a press cake, and then the dehydrated product such as a press cake is taken out from the solid-liquid separation device and then dehydrated. It is a form in which washing is performed by bringing the washing water into contact with the treated material.

第一の形態の洗浄工程において、水酸化チタンの凝集物の酸処理物と洗浄水を接触させた後は、フィルタープレス装置、遠心分離装置、液体サイクロン装置等の固液分離装置を用いて、水酸化チタンの凝集物の酸処理物と洗浄水を分離し、水酸化チタンの凝集物の酸処理物を得る。 In the cleaning step of the first embodiment, after the acid-treated product of the titanium hydroxide agglomerate is brought into contact with the cleaning water, a solid-liquid separation device such as a filter press device, a centrifugation device, or a liquid cyclone device is used. The acid-treated product of the titanium hydroxide agglomerates and the washing water are separated to obtain an acid-treated product of the titanium hydroxide agglomerates.

図4は、本発明の第一の形態のチタン成分の回収方法のうち、洗浄工程を行う他の形態の形態例を示すフロー図である。なお、ここでは中和剤として水酸化カルシウムを適用した形態を例に挙げて説明するが、本発明においては、酸化カルシウムを適用しても水酸化カルシウムを適用した場合と同様の効果が得られる。図4中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物を生じさせる。次いで、生じた水酸化チタンの凝集物を含む凝集処理液を、沈降槽5に移送し、沈降槽5内で、水酸化チタンの凝集物を沈降させて、沈降槽5の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出す。次いで、沈降槽5から抜き出した水酸化チタンの凝集物の沈降物を、沈降物貯蔵槽6に移送する。次いで、水酸化チタンの凝集物の沈降物を、フィルタープレス装置7を用いてろ過し、水酸化チタンの凝集物の沈降物から液相を除去して、水酸化チタンの凝集物をろ別し、水酸化チタンの凝集物のプレスケーキを得る。次いで、水酸化チタンの凝集物のプレスケーキを、酸処理槽8に移送し、酸処理槽8に塩酸14を供給して、水酸化チタンの凝集物と塩酸14を混合し、酸処理を施す。次いで、水酸化チタンの凝集物の酸処理物を、フィルタープレス装置9を用いてろ過し、水酸化チタンの凝集物の酸処理物から液相を除去した後、更に、フィルタープレス装置9内のろ過物に、0.2〜0.5MPaに加圧した洗浄水15を供給して、ろ過物に高圧で洗浄水15を接触させる貫通洗浄により、洗浄を行い、水酸化チタンの凝集物の酸処理物のプレスケーキ23を得る。 FIG. 4 is a flow chart showing a form example of another form in which the cleaning step is performed among the methods for recovering the titanium component of the first aspect of the present invention. Here, a form in which calcium hydroxide is applied as a neutralizing agent will be described as an example, but in the present invention, the same effect as when calcium hydroxide is applied can be obtained even if calcium oxide is applied. .. In FIG. 4, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and titanium hydroxide is agglomerated to generate agglomerates of titanium hydroxide. Let me. Next, the agglutination treatment liquid containing the generated titanium hydroxide agglomerates is transferred to the settling tank 5, and the titanium hydroxide agglomerates are settled in the settling tank 5 from the lower part or the bottom of the settling tank 5. Extract the sediment of titanium hydroxide agglomerates. Next, the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank 5 is transferred to the sediment storage tank 6. Next, the precipitate of the titanium hydroxide agglomerate is filtered using the filter press device 7, the liquid phase is removed from the precipitate of the titanium hydroxide agglomerate, and the titanium hydroxide agglomerate is filtered out. , Obtain a press cake of agglomerates of titanium hydroxide. Next, the press cake of the agglutinated titanium hydroxide is transferred to the acid treatment tank 8, the hydrochloric acid 14 is supplied to the acid treatment tank 8, the agglutinate of titanium hydroxide and the hydrochloric acid 14 are mixed, and the acid treatment is performed. .. Next, the acid-treated product of the titanium hydroxide agglomerates is filtered using the filter press device 9, the liquid phase is removed from the acid-treated product of the titanium hydroxide agglomerates, and then the inside of the filter press device 9 is further filtered. The wash water 15 pressurized to 0.2 to 0.5 MPa is supplied to the filter, and the filter is washed by penetrating wash in which the wash water 15 is brought into contact with the filter at high pressure, and the acid of the aggregate of titanium hydroxide is performed. A pressed cake 23 of the processed product is obtained.

つまり、洗浄工程の第二の形態は、工程(3A)を行い得られる水酸化チタンの凝集物の酸処理物を、フィルタープレス装置を用いるろ過により、水酸化チタンの凝集物を液相と分離し、更に、フィルタープレス装置内のろ過物に、0.2〜0.5MPaに加圧した洗浄水を供給して、ろ過物に高圧で洗浄水を接触させる貫通洗浄により、洗浄を行う形態である。 That is, in the second form of the cleaning step, the acid-treated product of the titanium hydroxide agglomerates obtained by performing the step (3A) is separated from the liquid phase by filtration using a filter press device. Further, the filter material in the filter press device is supplied with wash water pressurized to 0.2 to 0.5 MPa, and the filter material is brought into contact with the wash water at a high pressure for penetration cleaning. be.

洗浄工程において用いられる洗浄水のpHは、水酸化チタンを変質させずに洗浄できるpHであればよく、通常、6.0以上9.0以下である。また、水酸化チタンを変質させずに洗浄可能な洗浄水としては、特に限定されないが、例えば、イオン交換水、純水、超純水、工業用水、井戸水、水道水などを適用することができる。 The pH of the washing water used in the washing step may be any pH as long as it can be washed without deteriorating titanium hydroxide, and is usually 6.0 or more and 9.0 or less. The washing water that can be washed without deteriorating titanium hydroxide is not particularly limited, and for example, ion-exchanged water, pure water, ultrapure water, industrial water, well water, tap water, and the like can be applied. ..

洗浄時の温度は、特に制限されないが、10〜50℃であることが好ましく、15〜45℃であることがより好ましく、20〜40℃であることがさらに好ましい。 The temperature at the time of washing is not particularly limited, but is preferably 10 to 50 ° C, more preferably 15 to 45 ° C, and even more preferably 20 to 40 ° C.

洗浄工程を行った後は、固液分離装置を用いて、洗浄後の水酸化チタンの凝集物の酸処理物を含む洗浄処理液から液相を分離し、水酸化チタンの凝集物の脱水処理物を得、次いで、脱水処理物を60〜200℃で乾燥して、水酸化チタンの凝集物の酸処理物を得る。 After performing the cleaning step, a solid-liquid separator is used to separate the liquid phase from the cleaning solution containing the acid-treated product of the titanium hydroxide agglomerates after cleaning, and dehydration treatment of the titanium hydroxide agglomerates. The product is then dried at 60-200 ° C. to give an acid-treated product of agglomerates of titanium hydroxide.

本発明の第一の形態のチタン成分の回収方法において、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生する、チタン化合物を含む排液が、塩素を含有する場合、洗浄工程を行うことにより、水酸化チタンの凝集物中の塩素含有量を少なくすることができる。 In the method for recovering a titanium component according to the first aspect of the present invention, when the effluent containing a titanium compound generated when preparing a solid catalyst component for olefin polymerization or a catalyst for olefin polymerization contains chlorine. By performing the cleaning step, the chlorine content in the agglomerates of titanium hydroxide can be reduced.

本発明の第二の形態のチタン成分の回収方法は、工程(2)を行い生じる水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物に塩酸を接触させて、水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3B)を有する形態である。 In the method for recovering the titanium component of the second embodiment of the present invention, the titanium hydroxide agglomerates produced by performing step (2) are settled, and then hydrochloric acid is brought into contact with the settling of the titanium hydroxide agglomerates. It is a form having a step (3B) of performing acid treatment of agglomerates of titanium hydroxide to obtain an acid-treated product of agglomerates of titanium hydroxide.

すなわち、本発明の第二の形態のチタン成分の回収方法は、チタン化合物を含む排液からチタン成分を回収するチタン成分の回収方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)を行い生じる該水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物に塩酸を接触させて、水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3B)と、
を有すること、
を特徴とするチタン成分の回収方法である。本発明の第二の形態のチタン成分の回収方法は、工程(2)において水酸化チタンの凝集物を生じさせた後、凝集処理液から水酸化チタンの凝集物の沈降物を分離し、水酸化チタンの凝集物の沈降物中の液相を除去せずに、水酸化チタンの凝集物の沈降物に対し、酸処理を施す形態である。
That is, the method for recovering the titanium component according to the second aspect of the present invention is a method for recovering the titanium component from the effluent containing the titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. Step (2) to obtain agglomerates of titanium hydroxide by performing agglomeration treatment
After the titanium hydroxide agglomerates produced by performing the step (2) are precipitated, hydrochloric acid is brought into contact with the titanium hydroxide agglomerates to carry out acid treatment of the titanium hydroxide agglomerates with water. Step (3B) of obtaining an acid-treated product of titanium oxide agglomerates,
To have
It is a method for recovering a titanium component, which is characterized by the above. In the method for recovering the titanium component of the second aspect of the present invention, after the titanium hydroxide agglomerates are generated in the step (2), the sediment of the titanium hydroxide agglomerates is separated from the agglomeration treatment liquid, and water is used. This is a form in which the sediment of the titanium hydroxide aggregate is subjected to an acid treatment without removing the liquid phase in the precipitate of the titanium oxide aggregate.

本発明の第二の形態のチタン成分の回収方法について、図5を参照して説明する。図5は、本発明の第二の形態のチタン成分の回収方法の形態例のフロー図である。なお、ここでも中和剤として水酸化カルシウムを適用した形態を例に挙げて説明するが、本発明においては、中和剤として酸化カルシウムを適用しても、水酸化カルシウムを適用した場合と同様の効果が得られる。図5中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物を生じさせる。次いで、生じた水酸化チタンの凝集物を含む凝集処理液を、沈降槽5に移送し、沈降槽5内で、水酸化チタンの凝集物を沈降させて、沈降槽5の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出す。次いで、沈降槽5から抜き出した水酸化チタンの凝集物の沈降物を、酸処理槽18に移送し、酸処理槽18に塩酸14を供給して、水酸化チタンの凝集物の沈降物と塩酸14を混合し、酸処理を施す。次いで、水酸化チタンの凝集物の酸処理物を、フィルタープレス装置7を用いてろ過し、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別することにより、水酸化チタンの凝集物の酸処理物のプレスケーキ24を得る。 The method for recovering the titanium component of the second embodiment of the present invention will be described with reference to FIG. FIG. 5 is a flow chart of an example of a method for recovering a titanium component according to the second aspect of the present invention. Although a form in which calcium hydroxide is applied as a neutralizing agent will be described here as an example, in the present invention, even if calcium oxide is applied as a neutralizing agent, it is the same as when calcium hydroxide is applied. The effect of is obtained. In FIG. 5, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and titanium hydroxide is agglomerated to generate agglomerates of titanium hydroxide. Let me. Next, the agglutination treatment liquid containing the generated titanium hydroxide agglomerates is transferred to the settling tank 5, and the titanium hydroxide agglomerates are settled in the settling tank 5 from the lower part or the bottom of the settling tank 5. Extract the sediment of titanium hydroxide agglomerates. Next, the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank 5 is transferred to the acid treatment tank 18, and hydrochloric acid 14 is supplied to the acid treatment tank 18, and the sediment of the titanium hydroxide aggregate and hydrochloric acid are supplied. 14 is mixed and subjected to acid treatment. Next, the acid-treated product of the titanium hydroxide agglomerates is filtered using the filter press device 7, the liquid phase is removed from the acid-treated product of the titanium hydroxide agglomerates, and the acid of the titanium hydroxide agglomerates is removed. By filtering the treated product, a press cake 24 of an acid-treated product of agglomerates of titanium hydroxide is obtained.

本発明の第一の形態のチタン成分の回収方法は、工程(1)、工程(2)と、工程(3B)と、を有する。本発明の第二の形態のチタン成分の回収方法における工程(1)、工程(2)、用いる排水、処理及び処理方法等については、本発明のチタン化合物の回収方法と共通し、その詳細については、本発明のチタン成分の回収方法の説明で述べた通りである。 The method for recovering the titanium component according to the first aspect of the present invention includes steps (1), steps (2), and steps (3B). The steps (1), steps (2), wastewater used, treatment, treatment method, etc. in the titanium component recovery method of the second aspect of the present invention are common to the titanium compound recovery method of the present invention, and details thereof. Is as described in the description of the method for recovering the titanium component of the present invention.

本発明の第二の形態のチタン成分の回収方法に係る工程(3B)では、工程(2)を行い生じる水酸化チタンの凝集物を沈降させた後、得られる水酸化チタンの凝集物の沈降物に塩酸を接触させて、水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る。 In the step (3B) according to the method for recovering the titanium component of the second aspect of the present invention, the agglomerates of titanium hydroxide produced by performing the step (2) are settled, and then the agglomerates of titanium hydroxide obtained are settled. An acid-treated product of titanium hydroxide agglomerates is obtained by contacting an object with hydrochloric acid to obtain an acid-treated product of titanium hydroxide agglomerates.

工程(3B)において、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液から、水酸化チタンの凝集物の沈殿物を得る方法としては、特に制限されない。例えば、先ず、(i)工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液を、沈降槽に移送し、沈降槽内で、水酸化チタンの凝集物を沈降させる。次いで、(ii)沈降槽の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出し、沈降槽から抜き出した水酸化チタンの凝集物の沈降物を、酸処理槽に移送する方法が挙げられる。 In the step (3B), the method for obtaining a precipitate of the titanium hydroxide agglomerates from the agglutination treatment liquid containing the titanium hydroxide agglomerates after the step (2) is not particularly limited. For example, first, the agglutination treatment liquid containing the titanium hydroxide agglomerates after the step (i) (2) is transferred to a settling tank, and the titanium hydroxide agglomerates are settled in the settling tank. Next, (ii) a method of extracting the sediment of the titanium hydroxide aggregate from the lower part or the bottom of the sedimentation tank and transferring the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank to the acid treatment tank can be mentioned. Be done.

また、工程(3B)において、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液から、水酸化チタンの凝集物の沈降物を得る方法としては、工程(2)を行った後の水酸化チタンの凝集物を含む凝集処理液を、液体サイクロン、スクリューデカンタ等で処理して、凝集処理液から水相を分離し、水酸化チタンの凝集物の沈降物を得る方法が挙げられる。 Further, in the step (3B), as a method for obtaining a precipitate of the agglomerates of titanium hydroxide from the agglutination treatment liquid containing the agglutinates of titanium hydroxide after the step (2), the step (2) is performed. A method of treating the agglutination treatment liquid containing the agglutination of titanium hydroxide after the treatment with a liquid cyclone, a screw decanter, etc. to separate the aqueous phase from the agglutination treatment liquid to obtain a precipitate of the agglutination of titanium hydroxide. Can be mentioned.

工程(3B)では、次いで、水酸化チタンの凝集物の沈降物に、塩酸を接触させて、水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る。 In the step (3B), hydrochloric acid is then brought into contact with the precipitate of the titanium hydroxide agglutination to perform acid treatment of the titanium hydroxide agglutination to obtain an acid-treated product of the titanium hydroxide agglutination.

工程(3B)に係る酸処理では、水酸化チタンの凝集物の沈降物に、塩酸を接触させるが、このとき、液相のpHが5.0以下、好ましくは2.5以上4.5以下、より好ましくは3.0以上4.0以下となるように塩酸を接触させる。酸処理時の液相のpHが、上記範囲にあることにより、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。一方、酸処理時の液相のpHが上記範囲を超えると、水酸化チタンの凝集物中のカルシウム含有量を少なくする効果が得られ難くなる。 In the acid treatment according to the step (3B), hydrochloric acid is brought into contact with the precipitate of the aggregate of titanium hydroxide. At this time, the pH of the liquid phase is 5.0 or less, preferably 2.5 or more and 4.5 or less. , More preferably 3.0 or more and 4.0 or less. When the pH of the liquid phase during the acid treatment is in the above range, the calcium content in the titanium hydroxide agglutination can be reduced. On the other hand, if the pH of the liquid phase during the acid treatment exceeds the above range, it becomes difficult to obtain the effect of reducing the calcium content in the aggregate of titanium hydroxide.

工程(3B)に係る酸処理に用いられる酸は、塩酸である。塩酸は、酸処理を行った後の水酸化チタンの乾燥又は酸化の際に、生成物中から揮発して、除去されるので、酸処理に用いた酸が、生成物中に残留し難い。 The acid used for the acid treatment according to the step (3B) is hydrochloric acid. Hydrochloric acid is volatilized and removed from the product when the titanium hydroxide is dried or oxidized after the acid treatment, so that the acid used for the acid treatment is unlikely to remain in the product.

工程(3B)に係る酸処理に用いる塩酸の濃度は、特に制限されないが、1.0〜8.5mol/Lであることが好ましく、1.5〜7.0mol/Lであることが好ましく、2.7〜5.5mol/Lであることがより好ましい。酸処理に用いる塩酸の濃度が、上記範囲にあることにより、酸処理時の液相のpHを、容易に所望範囲に制御することができる。酸処理に用いる塩酸の濃度が、上記範囲を超えると酸処理時の液相のpHを制御し難くなり、また、上記範囲未満だと、円滑な酸処理を行い難くなる。 The concentration of hydrochloric acid used for the acid treatment according to the step (3B) is not particularly limited, but is preferably 1.0 to 8.5 mol / L, preferably 1.5 to 7.0 mol / L. It is more preferably 2.7 to 5.5 mol / L. When the concentration of hydrochloric acid used for the acid treatment is within the above range, the pH of the liquid phase during the acid treatment can be easily controlled within a desired range. If the concentration of hydrochloric acid used for the acid treatment exceeds the above range, it becomes difficult to control the pH of the liquid phase during the acid treatment, and if it is less than the above range, it becomes difficult to perform a smooth acid treatment.

工程(3B)に係る酸処理時の温度は、特に制限されないが、10〜50℃であることが好ましく、15〜45℃であることがより好ましく、20〜40℃であることがさらに好ましい。 The temperature during the acid treatment according to the step (3B) is not particularly limited, but is preferably 10 to 50 ° C, more preferably 15 to 45 ° C, and even more preferably 20 to 40 ° C.

工程(3B)に係る酸処理において、水酸化チタンの凝集物の沈降物と塩酸との接触時間は、60〜120分間であることが好ましく、60〜100分間であることがより好ましく、60〜80分間であることがさらに好ましい。 In the acid treatment according to the step (3B), the contact time between the precipitate of the titanium hydroxide aggregate and hydrochloric acid is preferably 60 to 120 minutes, more preferably 60 to 100 minutes, and 60 to 60 to 100 minutes. It is more preferably 80 minutes.

工程(3B)において、酸処理を行う方法としては、水酸化チタンの凝集物の沈降物に対して、酸処理槽中で塩酸を接触させて行うことが好ましい。 In the step (3B), as a method of performing the acid treatment, it is preferable to bring hydrochloric acid into contact with the sediment of the titanium hydroxide aggregate in the acid treatment tank.

工程(3B)において、酸処理を行って、水酸化チタンの凝集物の酸処理物を得た後は、固液分離装置を用いて、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物の脱水処理物を得、更に、脱水処理物を60〜200℃で乾燥して、水酸化チタンの凝集物の酸処理物を得る。この水酸化チタンの凝集物の酸処理物からの液相の除去及び乾燥により、水酸化チタンの凝集物の酸処理物から水及び塩化水素が除去され、水酸化チタンの凝集物の酸処理物が得られる。 In step (3B), after acid treatment is performed to obtain an acid-treated product of titanium hydroxide agglomerates, a liquid phase is prepared from the acid-treated product of titanium hydroxide agglomerates using a solid-liquid separator. It is removed to obtain a dehydrated product of the acid-treated product of the aggregate of titanium hydroxide, and further, the dehydrated product is dried at 60 to 200 ° C. to obtain an acid-treated product of the aggregate of titanium hydroxide. By removing the liquid phase from the acid-treated product of the titanium hydroxide agglomerates and drying, water and hydrogen chloride are removed from the acid-treated product of the titanium hydroxide agglomerates, and the acid-treated product of the titanium hydroxide agglomerates. Is obtained.

本発明の第二の形態のチタン成分の回収方法において、工程(3B)を行い得られる水酸化チタンは、Ti(OH)である。つまり、本発明のチタン成分の回収方法では、水酸化チタンの凝集物の状態で、チタン化合物を含む排液からチタン成分が回収される。そして、回収された水酸化チタンの凝集物(酸処理物)は、乾燥及び酸化後、酸化チタンに変換されて、種々のチタン化合物の製造原料として用いられる。 In the method for recovering the titanium component of the second aspect of the present invention, the titanium hydroxide obtained by performing the step (3B) is Ti (OH) 4 . That is, in the method for recovering the titanium component of the present invention, the titanium component is recovered from the effluent containing the titanium compound in the state of agglomerates of titanium hydroxide. Then, the recovered agglomerates of titanium hydroxide (acid-treated product) are converted into titanium oxide after drying and oxidation, and used as a raw material for producing various titanium compounds.

本発明の第二の形態のチタン成分の回収方法においては、チタン化合物を含む排水に対し、加水分解処理後、水酸化カルシウムを中和剤として用いて、特定のpHで一次中和処理及び二次中和処理、凝集処理を順次施し、水酸化チタンの凝集物を生じさせて沈降させ、得られる水酸化チタンの凝集物の沈降物に対し、塩酸を接触させる酸処理を施すことにより、酸処理を行い得られる水酸化チタンの凝集物中のカルシウム含有量を少なくすることができることから、カルシウム含有量が少ない水酸化チタンを回収することができる。本発明の第二の形態のチタン成分の回収方法では、工程(2)で生じた水酸化チタンの凝集物を沈降させた沈降物に対し、酸処理を行うことにより該水酸化チタンの凝集物に残存する水酸化カルシウム等の難水溶性未反応物質を溶解するので、水酸化チタンの凝集物中のカルシウム含有量を少なくすることができる。以上のことから、本発明の第二の形態のチタン成分の回収方法では、カルシウム含有量及び塩素含有量が少ない水酸化チタンを回収し得ると考えられる。 In the method for recovering the titanium component of the second embodiment of the present invention, the wastewater containing the titanium compound is subjected to a primary neutralization treatment at a specific pH by using calcium hydroxide as a neutralizing agent after the hydrolysis treatment. The next neutralization treatment and the agglomeration treatment are sequentially performed to generate and settle the agglomerates of titanium hydroxide, and the obtained precipitate of the agglomerates of titanium hydroxide is subjected to an acid treatment in which hydrochloric acid is brought into contact with the acid. Since the calcium content in the aggregate of titanium hydroxide obtained by the treatment can be reduced, the titanium hydroxide having a low calcium content can be recovered. In the method for recovering the titanium component according to the second aspect of the present invention, the agglomerates of titanium hydroxide produced in the step (2) are subjected to acid treatment on the settled precipitates to cause the agglomerates of titanium hydroxide. Since the poorly water-soluble unreacted substance such as calcium hydroxide remaining in the titanium hydroxide is dissolved, the calcium content in the agglomerates of titanium hydroxide can be reduced. From the above, it is considered that the titanium hydroxide component recovery method of the second aspect of the present invention can recover titanium hydroxide having a low calcium content and chlorine content.

本発明の第二の形態のチタン成分の回収方法は、工程(1)、工程(2)及び工程(3B)に加え、工程(3B)を行い得られる水酸化チタンの凝集物の酸処理物を、pH6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することができる。洗浄工程では、工程(3B)を行い得られる水酸化チタンの凝集物の酸処理物に洗浄水を接触させることにより、洗浄を行うが、水酸化チタンの凝集物の酸処理物と洗浄水の接触方法は、特に制限されず、例えば、以下の方法が挙げられる。 The method for recovering the titanium component according to the second aspect of the present invention is an acid-treated product of a titanium hydroxide agglomerate obtained by performing step (3B) in addition to step (1), step (2) and step (3B). Can have a washing step of washing with washing water having a pH of 6.0 or more and 9.0 or less. In the cleaning step, cleaning is performed by bringing the cleaning water into contact with the acid-treated product of the titanium hydroxide agglomerates obtained in step (3B). The contact method is not particularly limited, and examples thereof include the following methods.

図6は、本発明の第二の形態のチタン成分の回収方法のうち、洗浄工程を行う形態の形態例を示すフロー図である。図6中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物を生じさせる。次いで、生じた水酸化チタンの凝集物を含む凝集処理液を、沈降槽5に移送し、沈降槽5内で、水酸化チタンの凝集物を沈降させて、沈降槽5の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出す。次いで、沈降槽5から抜き出した水酸化チタンの凝集物の沈降物を、酸処理槽18に移送し、酸処理槽18に塩酸14を供給して、水酸化チタンの凝集物の沈降物と塩酸14を混合し、酸処理を施す。次いで、水酸化チタンの凝集物の酸処理物を、フィルタープレス装置7を用いてろ過し、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別することにより、水酸化チタンの凝集物の酸処理物のプレスケーキを得る。次いで、水酸化チタンの凝集物の酸処理物のプレスケーキを、洗浄槽32に移送し、洗浄槽槽32に洗浄水15を供給して、水酸化チタンの凝集物の酸処理物と洗浄水15を混合し、洗浄を行う。次いで、水酸化チタンの凝集物の酸処理物の洗浄物を、フィルタープレス装置33を用いてろ過し、水酸化チタンの凝集物の酸処理物の洗浄物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別することにより、水酸化チタンの凝集物の酸処理物のプレスケーキ25を得る。 FIG. 6 is a flow chart showing an example of a form in which a cleaning step is performed among the methods for recovering a titanium component according to the second aspect of the present invention. In FIG. 6, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and titanium hydroxide is agglomerated to generate agglomerates of titanium hydroxide. Let me. Next, the agglutination treatment liquid containing the generated titanium hydroxide agglomerates is transferred to the settling tank 5, and the titanium hydroxide agglomerates are settled in the settling tank 5 from the lower part or the bottom of the settling tank 5. Extract the sediment of titanium hydroxide agglomerates. Next, the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank 5 is transferred to the acid treatment tank 18, and hydrochloric acid 14 is supplied to the acid treatment tank 18, and the sediment of the titanium hydroxide aggregate and hydrochloric acid are supplied. 14 is mixed and subjected to acid treatment. Next, the acid-treated product of the titanium hydroxide agglomerates is filtered using the filter press device 7, the liquid phase is removed from the acid-treated product of the titanium hydroxide agglomerates, and the acid of the titanium hydroxide agglomerates is removed. By filtering the treated product, a press cake of an acid-treated product of agglomerates of titanium hydroxide is obtained. Next, the press cake of the acid-treated product of the titanium hydroxide agglomerates is transferred to the washing tank 32, and the washing water 15 is supplied to the washing tank tank 32 to supply the acid-treated product of the titanium hydroxide agglomerates and the washing water. 15 is mixed and washed. Next, the washed product of the acid-treated product of the agglomerates of titanium hydroxide is filtered using the filter press device 33, the liquid phase is removed from the washed product of the acid-treated product of the aggregates of titanium hydroxide, and hydroxylation is performed. By filtering the acid-treated product of the titanium agglomerates, a press cake 25 of the acid-treated product of the titanium hydroxide agglomerates is obtained.

つまり、洗浄工程の第一の形態は、工程(3B)を行い得られる水酸化チタンの凝集物の酸処理物を、フィルタープレス装置、遠心分離装置、液体サイクロン装置等の固液分離装置を用いて、水酸化チタンの凝集物の酸処理物を液相と分離し、プレスケーキ等の脱水処理物を得、次いで、プレスケーキ等の脱水処理物を、洗浄水を固液分離装置から取り出し、次いで、脱水処理物に洗浄水を接触させることにより、洗浄を行う形態である。 That is, in the first form of the cleaning step, the acid-treated product of the aggregate of titanium hydroxide obtained in the step (3B) is subjected to a solid-liquid separation device such as a filter press device, a centrifugation device, or a liquid cyclone device. Then, the acid-treated product of the aggregate of titanium hydroxide is separated from the liquid phase to obtain a dehydrated product such as a press cake, and then the dehydrated product such as a press cake is taken out from the solid-liquid separation device with washing water. Next, the dehydrated product is brought into contact with the washing water for washing.

第一の形態の洗浄工程において、水酸化チタンの凝集物の酸処理物と洗浄水を接触させた後は、フィルタープレス装置、遠心分離装置、液体サイクロン装置等の固液分離装置を用いて、水酸化チタンの凝集物の酸処理物と洗浄水を分離し、水酸化チタンの凝集物の酸処理物を得る。 In the cleaning step of the first embodiment, after the acid-treated product of the titanium hydroxide agglomerate is brought into contact with the cleaning water, a solid-liquid separation device such as a filter press device, a centrifugation device, or a liquid cyclone device is used. The acid-treated product of the titanium hydroxide agglomerates and the washing water are separated to obtain an acid-treated product of the titanium hydroxide agglomerates.

図7は、本発明の第二の形態のチタン成分の回収方法のうち、洗浄工程を行う他の形態の形態例を示すフロー図である。図7中、受水槽1に、チタン化合物を含む排液10を移送し、受水槽1内に水11を供給して、チタン化合物を含む排液10と水11を混合し、加水分解処理を施す。次いで、加水分解処理された処理液を、一次中和処理槽2に移送し、一次中和処理槽2に水酸化カルシウム懸濁液12を供給して、一次中和処理槽2内の処理液のpHが1.5以上2.5未満になるように一次中和処理を施す。次いで、一次中和処理を施した処理液を、二次中和処理槽3に移送し、二次中和処理槽3に水酸化カルシウム懸濁液13を供給して、二次中和処理槽3内の処理液のpHが6.5以上7.5以下になるように二次中和処理を施す。次いで、二次中和処理を施した処理液を、凝集槽4に移送して、凝集槽4に凝集剤を添加して、水酸化チタンを凝集させることにより、水酸化チタンの凝集物を生じさせる。次いで、生じた水酸化チタンの凝集物を含む凝集処理液を、沈降槽5に移送し、沈降槽5内で、水酸化チタンの凝集物を沈降させて、沈降槽5の下部又は底部から、水酸化チタンの凝集物の沈降物を抜き出す。次いで、沈降槽5から抜き出した水酸化チタンの凝集物の沈降物を、酸処理槽18に移送し、酸処理槽18に塩酸14を供給して、水酸化チタンの凝集物の沈降物と塩酸14を混合し、酸処理を施す。次いで、水酸化チタンの凝集物の酸処理物を、フィルタープレス装置7を用いてろ過し、水酸化チタンの凝集物の酸処理物から液相を除去して、水酸化チタンの凝集物の酸処理物をろ別することにより、水酸化チタンの凝集物の酸処理物から液相を除去した後、更に、フィルタープレス装置7内のろ過物に、0.2〜0.5MPaに加圧した洗浄水15を供給して、ろ過物に高圧で洗浄水15を接触させる貫通洗浄により、洗浄を行い、水酸化チタンの凝集物の酸処理物のプレスケーキ26を得る。 FIG. 7 is a flow chart showing a form example of another form in which the cleaning step is performed among the methods for recovering the titanium component of the second form of the present invention. In FIG. 7, the drainage 10 containing the titanium compound is transferred to the water receiving tank 1, water 11 is supplied into the water receiving tank 1, the drainage 10 containing the titanium compound and the water 11 are mixed, and hydrolysis treatment is performed. Give. Next, the hydrolyzed treatment liquid is transferred to the primary neutralization treatment tank 2, the calcium hydroxide suspension 12 is supplied to the primary neutralization treatment tank 2, and the treatment liquid in the primary neutralization treatment tank 2 is supplied. The primary neutralization treatment is performed so that the pH of the calcium hydroxide is 1.5 or more and less than 2.5. Next, the treatment liquid subjected to the primary neutralization treatment is transferred to the secondary neutralization treatment tank 3, the calcium hydroxide suspension 13 is supplied to the secondary neutralization treatment tank 3, and the secondary neutralization treatment tank 3 is supplied. Secondary neutralization treatment is performed so that the pH of the treatment liquid in 3 is 6.5 or more and 7.5 or less. Next, the treatment liquid subjected to the secondary neutralization treatment is transferred to the coagulation tank 4, a coagulant is added to the coagulation tank 4, and titanium hydroxide is agglomerated to generate agglomerates of titanium hydroxide. Let me. Next, the agglutination treatment liquid containing the generated titanium hydroxide agglomerates is transferred to the settling tank 5, and the titanium hydroxide agglomerates are settled in the settling tank 5 from the lower part or the bottom of the settling tank 5. Extract the sediment of titanium hydroxide agglomerates. Next, the sediment of the titanium hydroxide aggregate extracted from the sedimentation tank 5 is transferred to the acid treatment tank 18, and hydrochloric acid 14 is supplied to the acid treatment tank 18, and the sediment of the titanium hydroxide aggregate and hydrochloric acid are supplied. 14 is mixed and subjected to acid treatment. Next, the acid-treated product of the titanium hydroxide aggregate is filtered using the filter press device 7, the liquid phase is removed from the acid-treated product of the titanium hydroxide aggregate, and the acid of the titanium hydroxide aggregate is removed. The liquid phase was removed from the acid-treated product of the aggregate of titanium hydroxide by filtering the treated product, and then the filtered product in the filter press device 7 was further pressurized to 0.2 to 0.5 MPa. The washing is performed by penetrating washing in which the washing water 15 is supplied and the washing water 15 is brought into contact with the filter medium at high pressure to obtain a press cake 26 which is an acid-treated product of agglomerates of titanium hydroxide.

つまり、洗浄工程の第二の形態は、工程(3B)を行い得られる水酸化チタンの凝集物の酸処理物を、フィルタープレス装置を用いるろ過により、水酸化チタンの凝集物を液相と分離し、更に、フィルタープレス装置内のろ過物に、0.2〜0.5MPaに加圧した洗浄水を供給して、ろ過物に高圧で洗浄水を接触させる貫通洗浄により、洗浄を行う形態である。 That is, in the second form of the cleaning step, the acid-treated product of the titanium hydroxide agglomerates obtained by performing the step (3B) is separated from the liquid phase by filtration using a filter press device. Further, the filter material in the filter press device is supplied with wash water pressurized to 0.2 to 0.5 MPa, and the filter material is brought into contact with the wash water at a high pressure for penetration cleaning. be.

洗浄工程において用いられる洗浄水のpHは、水酸化チタンを変質させずに洗浄できるpHであればよく、通常、6.0以上9.0以下である。また、水酸化チタンを変質させずに洗浄可能な洗浄水としては、特に限定されないが、例えば、イオン交換水、純水、超純水、工業用水、井戸水、水道水などを適用することができる。 The pH of the washing water used in the washing step may be any pH as long as it can be washed without deteriorating titanium hydroxide, and is usually 6.0 or more and 9.0 or less. The washing water that can be washed without deteriorating titanium hydroxide is not particularly limited, and for example, ion-exchanged water, pure water, ultrapure water, industrial water, well water, tap water, and the like can be applied. ..

洗浄時の温度は、特に制限されないが、10〜50℃であることが好ましく、15〜45℃であることがより好ましく、20〜40℃であることがさらに好ましい。 The temperature at the time of washing is not particularly limited, but is preferably 10 to 50 ° C, more preferably 15 to 45 ° C, and even more preferably 20 to 40 ° C.

洗浄工程を行った後は、固液分離装置を用いて、洗浄後の水酸化チタンの凝集物の酸処理物を含む洗浄処理液から液相を分離し、水酸化チタンの凝集物の脱水処理物を得、次いで、脱水処理物を60〜200℃で乾燥して、水酸化チタンの凝集物の酸処理物を得る。 After performing the cleaning step, a solid-liquid separator is used to separate the liquid phase from the cleaning solution containing the acid-treated product of the titanium hydroxide agglomerates after cleaning, and dehydration treatment of the titanium hydroxide agglomerates. The product is then dried at 60-200 ° C. to give an acid-treated product of agglomerates of titanium hydroxide.

本発明の第二の形態のチタン成分の回収方法において、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生する、チタン化合物を含む排液が、塩素を含有する場合、洗浄工程を行うことにより、水酸化チタンの凝集物中の塩素含有量を少なくすることができる。 In the method for recovering the titanium component of the second embodiment of the present invention, when the effluent containing the titanium compound generated when preparing the solid catalyst component for olefin polymerization or the catalyst for olefin polymerization contains chlorine. By performing the cleaning step, the chlorine content in the agglomerates of titanium hydroxide can be reduced.

このようにして、本発明のチタン成分の回収方法では、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタン化合物を含む排液中のチタン化合物を、水酸化チタンとして回収することができ、カルシウム含有量が少ない水酸化チタンを、高い収率で簡便に回収することができる。 In this way, in the method for recovering the titanium component of the present invention, the titanium compound in the effluent containing the titanium compound generated when the solid catalyst component for olefin polymerization or the catalyst for olefin polymerization is prepared is titanium hydroxide. Titanium hydroxide, which has a low calcium content, can be easily recovered in a high yield.

次に、本発明の酸化チタンの製造方法について説明する。
本発明の酸化チタンの製造方法は、チタン化合物を含む排液から酸化チタンを製造する酸化チタンの製造方法であって、
該チタン化合物を含む排液を水と接触させ、該チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を施し、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、酸処理物を得る工程(3)と、
該水酸化チタンの凝集物を酸化して、酸化チタンを得る酸化工程と、
を有すること、
を特徴とする。また、本発明の酸化チタンの製造方法は、工程(3)を行い得られる水酸化チタンの凝集物の酸処理物を、pH6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することができる。
Next, the method for producing titanium oxide of the present invention will be described.
The method for producing titanium oxide of the present invention is a method for producing titanium oxide from a effluent containing a titanium compound.
The step (1) of bringing the effluent containing the titanium compound into contact with water and hydrolyzing the titanium compound.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. The step (2) of obtaining an agglomerate of titanium hydroxide by subjecting the agglomeration treatment to the agglomerate.
In the step after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the aggregate of titanium hydroxide to obtain an acid-treated product, and the step (3).
An oxidation step of oxidizing the titanium hydroxide aggregate to obtain titanium oxide,
To have
It is characterized by. Further, the method for producing titanium oxide of the present invention includes a washing step of washing the acid-treated product of the aggregate of titanium hydroxide obtained by performing the step (3) with washing water having a pH of 6.0 or more and 9.0 or less. be able to.

本発明の酸化チタンの製造方法は、水酸化チタンの凝集物の酸処理物を酸化して、酸化チタンを得る酸化工程を有すること以外は、工程(1)、工程(2)、工程(3)、工程(3A)、工程(3B)、洗浄工程、用いる排水、処理及び処理方法等については、本発明のチタン化合物の回収方法と共通し、その詳細については、本発明のチタン成分の回収方法の説明で述べた通りである。 The method for producing titanium oxide of the present invention includes steps (1), steps (2), and steps (3), except that it has an oxidation step of oxidizing an acid-treated product of titanium hydroxide agglomerates to obtain titanium oxide. ), Step (3A), Step (3B), Cleaning step, Wastewater used, Treatment and treatment method, etc. are common to the method for recovering the titanium compound of the present invention. As described in the explanation of the method.

本発明の酸化チタンの製造方法に係る酸化工程は、水酸化チタンの凝集物の酸処理物を酸化することにより、酸化チタンを得る工程である。 The oxidation step according to the method for producing titanium oxide of the present invention is a step of obtaining titanium oxide by oxidizing an acid-treated product of agglomerates of titanium hydroxide.

酸化工程における酸化条件としては、特に制限されず、水酸化チタンが酸化され酸化チタンに変換される条件であればよい。例えば、酸化工程における酸化反応温度は、好ましくは60〜1000℃である。また、酸化反応時間は、適宜選択される。また、酸化反応雰囲気は、大気雰囲気下、酸素ガス雰囲気下等の酸化性雰囲気下である。また、酸化工程では、酸化を1回だけ行ってもよいし、あるいは、酸化を2回以上、同じ温度又は異なる温度で行ってもよい。 The oxidation conditions in the oxidation step are not particularly limited as long as they are conditions in which titanium hydroxide is oxidized and converted to titanium oxide. For example, the oxidation reaction temperature in the oxidation step is preferably 60 to 1000 ° C. The oxidation reaction time is appropriately selected. The oxidation reaction atmosphere is an oxidizing atmosphere such as an atmospheric atmosphere and an oxygen gas atmosphere. Further, in the oxidation step, oxidation may be performed only once, or oxidation may be performed twice or more at the same temperature or different temperatures.

本発明の酸化チタンの製造方法では、工程(1)及び工程(2)を行い得られる水酸化チタンの凝集物に対し工程(3)を行うので、チタン化合物を含む排液から、チタン成分を回収し、水酸化チタンを得る際に、中和剤として水酸化カルシウムを用いても、カルシウム含有量が少ない水酸化チタンを得ることができるので、カルシウム含有量が少ない酸化チタンを得ることができる。また、本発明の酸化チタンの製造方法では、更に、洗浄工程を行うことにより、チタン化合物を含む排液が、塩素を含有する場合、酸化チタン中の塩素含有量を低くすることができる。 In the method for producing titanium oxide of the present invention, since the step (3) is performed on the aggregate of titanium hydroxide obtained by performing the steps (1) and (2), the titanium component is removed from the effluent containing the titanium compound. Even if calcium hydroxide is used as a neutralizing agent when recovering and obtaining titanium hydroxide, titanium hydroxide having a low calcium content can be obtained, so that titanium oxide having a low calcium content can be obtained. .. Further, in the method for producing titanium oxide of the present invention, the chlorine content in titanium oxide can be lowered when the effluent containing the titanium compound contains chlorine by further performing a cleaning step.

このようにして、本発明の酸化チタンの製造方法では、チタン化合物を含む排液中のチタン化合物を、酸化チタンとして回収することができ、且つ、カルシウム含有量が少ない酸化チタンを、洗浄工程を行う場合は、カルシウム含有量が少なく且つ塩素含有量が少ない酸化チタンを、簡便に回収することができる。 In this way, in the method for producing titanium oxide of the present invention, the titanium compound in the effluent containing the titanium compound can be recovered as titanium oxide, and the titanium oxide having a low calcium content can be cleaned. When this is done, titanium oxide having a low calcium content and a low chlorine content can be easily recovered.

次に、本発明のチタン酸アルカリ金属の製造方法について説明する。
本発明のチタン酸アルカリ金属の製造方法は、本発明のチタン成分の回収方法で回収された水酸化チタン、又は本発明の酸化チタンの製造方法を行い得られた酸化チタンを原料として用いることを特徴とするものである。
Next, the method for producing the alkali metal titanate of the present invention will be described.
In the method for producing an alkali metal titanate of the present invention, titanium hydroxide recovered by the method for recovering a titanium component of the present invention or titanium oxide obtained by the method for producing titanium oxide of the present invention is used as a raw material. It is a feature.

本発明のチタン酸アルカリ金属の製造方法は、原料として、本発明のチタン成分の回収方法で回収された水酸化チタン、又は本発明の酸化チタンの製造方法を行い得られた酸化チタンを原料として用いることを除けば、公知の方法を採用することができる。 The method for producing an alkali metal titanate of the present invention uses titanium hydroxide recovered by the method for recovering a titanium component of the present invention or titanium oxide obtained by the method for producing titanium oxide of the present invention as a raw material. A known method can be adopted except that it is used.

例えば、チタン原料として、本発明のチタン成分の回収方法で回収された水酸化チタンを用いる場合は、適宜の方法で、水酸化チタンを酸化して、酸化チタンに変換した後、得られる酸化チタンを、チタン原料として用いるとともに、アルカリ原料として、カリウム化合物を用い、両者を含む原料混合物を焼成処理し、粉砕処理することにより、チタン酸アルカリ金属を製造することができる。また、チタン原料として、本発明の酸化チタンの製造方法を行い得られた酸化チタンを用いる場合は、本発明の酸化チタンの製造方法を行い得られた酸化チタンを、チタン原料として用いるとともに、アルカリ原料として、カリウム化合物を用い、両者を含む原料混合物を焼成処理し、粉砕処理することにより、チタン酸アルカリ金属を製造することができる。 For example, when titanium hydroxide recovered by the method for recovering a titanium component of the present invention is used as a titanium raw material, titanium oxide obtained after oxidizing titanium hydroxide to titanium oxide by an appropriate method is used. Is used as a titanium raw material, and a potassium compound is used as an alkaline raw material, and a raw material mixture containing both is fired and pulverized to produce an alkali metal titanate. When titanium oxide obtained by the method for producing titanium oxide of the present invention is used as the titanium oxide raw material, the titanium oxide obtained by the method for producing titanium oxide of the present invention is used as a titanium oxide raw material and is alkaline. An alkali metal titanate can be produced by using a potassium compound as a raw material and firing and pulverizing a raw material mixture containing both of them.

得られたチタン酸アルカリ金属は、例えば、自動車、鉄道車両、航空機および産業機械類等における制動装置を構成する、ブレーキライニング、ディスクパッド、クラッチフェージング等の摩擦摺動部材用の摩擦材として好適に用いられる。 The obtained alkali metal titanate is suitable as a friction material for friction sliding members such as brake linings, disc pads, and clutch fading, which constitute a braking device in, for example, automobiles, railroad vehicles, aircraft, industrial machinery, and the like. Used.

本発明のチタン酸アルカリ金属の製造方法によれば、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタン化合物含有排液から、得られたカルシウム含有量が少ない高純度なチタン化合物を原料に用いることから、高純度なチタン酸アルカリ金属を低コストで製造することができる。 According to the method for producing an alkali metal titanate of the present invention, a high calcium content obtained from a titanium compound-containing effluent generated when preparing a solid catalyst component for olefin polymerization or a catalyst for olefin polymerization is high. Since a pure titanium compound is used as a raw material, a high-purity alkali metal titanate can be produced at low cost.

次に、実施例および比較例を挙げて本発明を更に具体的に説明するが、本発明は、以下の例により何ら制限されるものではない。 Next, the present invention will be described in more detail with reference to Examples and Comparative Examples, but the present invention is not limited to the following examples.

(実施例1)
<酸化チタンの合成>
図2に示す処理フローを用いて、チタン化合物を含む排液から酸化チタンを得た。
すなわち、チーグラーナッタ触媒の製造工場において、オレフィン類重合用固体触媒成分を調製した際に発生する、四塩化チタン、ジエトキシマグネシウム、トルエンおよびヘプタンを含む液温25℃の排液を処理対象とし、当該排液を容量250mの受水槽1に送入することで混合し、加水分解を施した。このとき、受水槽中の排液のpHが1になるように受水槽中に加水分解用の水11を送入した。
上記加水分解処理された処理液を、10m/hの速度で容量10mの一次中和処理槽2に送入し、液温25℃の12.5mol/L水酸化カルシウム水溶液を用いて、一次中和処理槽2内に送入された処理液のpHが2.0になるように一次中和処理を施した。
次いで、上記一次中和処理を施した処理液を、10m/hの速度で容量10mの二次中和処理槽3に送入し、液温25℃の12.5mol/L水酸化カルシウム水溶液を用いて、二次中和処理槽3内に送入された処理液のpHが7.2になるように二次中和処理を施した。
二次中和処理を施した液温25℃の処理液は、10m/hの速度で容量10mの凝集槽4内に送入して、凝集剤(クリタ・ケミカル北陸(株)製クリファームPA−833)を用いて凝集させて凝集処理液を得た後、該凝集処理液を、沈降槽5に移送し、沈降槽5内で沈降させて、沈降槽5から沈降物を抜き出した。次いで、沈降槽5から抜き出した沈降物を、沈降物貯蔵槽6に移送し、該沈降物をフィルタープレス装置7を用いてろ過し、該沈降物から液相を除去して凝集物をろ別し、該凝集物のプレスケーキを得た。次いで、該凝集物のプレスケーキ530kgを、酸処理槽8に移送し、イオン交換水26500kgで希釈した。得られた液相のpHが5.0になるように酸処理槽8に塩酸14を供給して、該凝集物と塩酸14を混合し、酸処理を施した。次いで、酸処理を施して得られた酸処理物を、フィルタープレス装置9を用いてろ過し、該酸処理物から液相を除去して、該酸処理物をろ別し、該酸処理物のプレスケーキ21を得た。該プレスケーキ21を、熱風循環乾燥機を用いて180℃、16時間の条件で乾燥し、プレスケーキ21の乾燥物(水酸化チタン)を得た。次いで、得られたプレスケーキ21の乾燥物(水酸化チタン)を、シャトルキルンを用いて大気雰囲気中で850℃、2時間加熱処理を施した後、950℃、2時間さらに加熱処理を施して、目的とする酸化チタンを得た。
得られた水酸化チタンおよび酸化チタンの結晶構造を、X’PERT−PRO−MPD多目的X線回析装置(PANalytical製)を用いて測定したところ、得られた水酸化チタンは少量のルチル型の酸化チタンを含むが主たる結晶系が非晶質であるのに対し、酸化チタンはルチル型であることが確認できた。
(Example 1)
<Synthesis of titanium oxide>
Using the treatment flow shown in FIG. 2, titanium oxide was obtained from the effluent containing a titanium compound.
That is, the wastewater containing titanium tetrachloride, diethoxymagnesium, toluene and heptane, which is generated when the solid catalyst component for olefin polymerization is prepared in the Ziegler-Natta catalyst manufacturing plant, is treated. The drainage was mixed by feeding it into a water receiving tank 1 having a capacity of 250 m 3, and hydrolyzed. At this time, water 11 for hydrolysis was sent into the water receiving tank so that the pH of the drainage liquid in the water receiving tank became 1.
The hydrolyzed treatment liquid was fed into a primary neutralization treatment tank 2 having a capacity of 10 m 3 at a rate of 10 m 3 / h, and a 12.5 mol / L calcium hydroxide aqueous solution having a liquid temperature of 25 ° C. was used. The primary neutralization treatment was performed so that the pH of the treatment liquid fed into the primary neutralization treatment tank 2 became 2.0.
Next, the treatment liquid subjected to the above primary neutralization treatment was fed into the secondary neutralization treatment tank 3 having a capacity of 10 m 3 at a rate of 10 m 3 / h, and 12.5 mol / L calcium hydroxide having a liquid temperature of 25 ° C. Using an aqueous solution, the secondary neutralization treatment was performed so that the pH of the treatment liquid fed into the secondary neutralization treatment tank 3 became 7.2.
The treated liquid having been subjected to the secondary neutralization treatment and having a liquid temperature of 25 ° C. is fed into the coagulation tank 4 having a capacity of 10 m 3 at a speed of 10 m 3 / h, and is used as a coagulant (Kurita Chemical Hokuriku Co., Ltd. After aggregating using the farm PA-833) to obtain a coagulation treatment liquid, the coagulation treatment liquid was transferred to the settling tank 5 and settled in the settling tank 5, and the settling material was extracted from the settling tank 5. .. Next, the sediment extracted from the sedimentation tank 5 is transferred to the sediment storage tank 6, the sediment is filtered using the filter press device 7, the liquid phase is removed from the sediment, and the agglomerates are filtered. Then, a press cake of the agglomerate was obtained. Next, 530 kg of the agglutinated press cake was transferred to the acid treatment tank 8 and diluted with 26,500 kg of ion-exchanged water. Hydrochloric acid 14 was supplied to the acid treatment tank 8 so that the pH of the obtained liquid phase was 5.0, and the aggregate and hydrochloric acid 14 were mixed and subjected to acid treatment. Next, the acid-treated product obtained by subjecting the acid treatment is filtered using a filter press device 9, the liquid phase is removed from the acid-treated product, the acid-treated product is filtered off, and the acid-treated product is filtered. Press cake 21 was obtained. The press cake 21 was dried at 180 ° C. for 16 hours using a hot air circulation dryer to obtain a dried product (titanium hydroxide) of the press cake 21. Next, the obtained dried product (titanium hydroxide) of the press cake 21 was heat-treated at 850 ° C. for 2 hours in an air atmosphere using a shuttle kiln, and then further heat-treated at 950 ° C. for 2 hours. , The target titanium oxide was obtained.
When the crystal structures of the obtained titanium hydroxide and titanium oxide were measured using an X'PERT-PRO-MPD multipurpose X-ray diffractometer (manufactured by PANICAL), the obtained titanium hydroxide was of a rutile type in a small amount. It was confirmed that titanium oxide is a rutile type, whereas titanium oxide is contained but the main crystal system is amorphous.

<チタン酸カリウムの合成>
得られた酸化チタン52.16kgと、チタン鉱石52.23kg、炭酸カリウム粉末32.28kg、チタン粉末2.87kgおよび、木屑(木質ペレット)5.7kgを、振動ロッドミル(中央化工機株式会社製)中に充填し、さらにここに低級アルコールを0.6kg添加して、振幅5mmで15分間処理することにより、原料混合物を得た。
上記の原料混合物145kgを、温度1170℃のロータリーキルンへ14.4kg/hrの流量で供給した。このロータリーキルン内でチタン酸カリウムへの合成反応が起こり、焼成物となってロータリーキルンから排出された。排出された焼成物を室温まで急冷した。
その後、冷却した焼成物を振動ロッドミル(中央化工機株式会社製)で粉砕した後、分級機を内蔵した衝撃式粉砕機(ホソカワミクロン株式会社製、ACMパルベライザ)で粉砕し、チタン酸カリウム粒子を得た。得られたチタン酸カリウム粒子の各物性を表1に示す。また、走査型電子顕微鏡観察結果(SEM)を図8に示す。
なお、比較のため、表1には市販のチタン酸カリウム粒子(東邦チタニウム株式会社製、TOFIX−SNR−S)の各物性も示した。また、走査型電子顕微鏡観察結果(SEM)を図9に示す。
各物性の測定に用いた測定装置又は測定方法は以下の通りである。
<測定装置>
XRD:X’PERT−PRO−MPD多目的X線回析装置(PANalytical製)
SEM:JSM−7800(日本電子製)
比表面積:monosorb(quantacrome社製)
平均粒径:PITA−3(株式会社セイシン企業製)
<Synthesis of potassium titanate>
52.16 kg of the obtained titanium oxide, 52.23 kg of titanium ore, 32.28 kg of potassium carbonate powder, 2.87 kg of titanium powder, and 5.7 kg of wood chips (wood pellets) were added to a vibrating rod mill (manufactured by Chuo Kakoki Co., Ltd.). The mixture was filled therein, and 0.6 kg of lower alcohol was further added thereto, and the mixture was treated with an amplitude of 5 mm for 15 minutes to obtain a raw material mixture.
145 kg of the above raw material mixture was supplied to a rotary kiln at a temperature of 1170 ° C. at a flow rate of 14.4 kg / hr. A synthetic reaction to potassium titanate occurred in this rotary kiln, and it became a fired product and was discharged from the rotary kiln. The discharged fired product was rapidly cooled to room temperature.
Then, the cooled calcined product is crushed with a vibrating rod mill (manufactured by Chuo Kakoki Co., Ltd.) and then crushed with an impact type crusher (manufactured by Hosokawa Micron Co., Ltd., ACM Pulverizer) with a built-in classifier to obtain potassium titanate particles. rice field. Table 1 shows the physical characteristics of the obtained potassium titanate particles. The scanning electron microscope observation result (SEM) is shown in FIG.
For comparison, Table 1 also shows the physical characteristics of commercially available potassium titanate particles (TOFIX-SNR-S manufactured by Toho Titanium Co., Ltd.). The scanning electron microscope observation result (SEM) is shown in FIG.
The measuring device or measuring method used for measuring each physical property is as follows.
<Measuring device>
XRD: X'PERT-PRO-MPD multipurpose X-ray diffractometer (manufactured by PANalytical)
SEM: JSM-7800 (manufactured by JEOL Ltd.)
Specific surface area: monosorb (manufactured by quantachrome)
Average particle size: PITA-3 (manufactured by Seishin Enterprise Co., Ltd.)

Figure 0006959471
1)6KTO:6チタン酸カリウム
Figure 0006959471
1) 6KTO: Potassium 6 titanate

表1に示した通り、実施例1のチタン酸カリウム粒子は、市販品と比較して、同じ相構成及び粉末形状を有していることが確認できた。また、比表面積(規格値:2〜3m/g)、平均粒径(規格値:25〜60μm)についても、市販品の規格値内であった。 As shown in Table 1, it was confirmed that the potassium titanate particles of Example 1 had the same phase composition and powder shape as those of the commercially available product. The specific surface area (standard value: 2 to 3 m 2 / g) and average particle size (standard value: 25 to 60 μm) were also within the standard values of commercially available products.

(試験例1〜試験例5)
実施例1と同様にして得られた凝集物のプレスケーキ(PC)を、酸処理槽8に移送し、イオン交換水で希釈した。得られた希釈液のpHが表2に記載の所定値になるように酸処理槽8に塩酸14を供給して、所定時間撹拌して該凝集物と塩酸14を混合し、酸処理を施した(試験例3〜5)。なお、試験例1及び2では、塩酸を混合しなかった。
次いで、酸処理を施して得られた酸処理物を、フィルタープレス装置9を用いてろ過し、該酸処理物から液相を除去して、該酸処理物をろ別し、該酸処理物のプレスケーキ21を得た。該プレスケーキ21を、所定条件で乾燥し、プレスケーキ21の乾燥物(水酸化チタン)を得た。なお、凝集物のプレスケーキからプレスケーキ21の乾燥物(水酸化チタン)を合成するための各条件は、表2に示した通りである。また、得られたプレスケーキ21の乾燥物(水酸化チタン)について、ICP発光分光分析法(Inductivity coupled plasma optical emission spectrometer;ICP−OES)を用い、塩素(Cl)及びカルシウム(Ca)の含有量を測定した結果もあわせて表2に示した。
(Test Examples 1 to 5)
The agglutinated press cake (PC) obtained in the same manner as in Example 1 was transferred to the acid treatment tank 8 and diluted with ion-exchanged water. Hydrochloric acid 14 is supplied to the acid treatment tank 8 so that the pH of the obtained diluted solution becomes the predetermined value shown in Table 2, and the mixture is stirred for a predetermined time to mix the agglomerate and hydrochloric acid 14 and subjected to acid treatment. (Test Examples 3 to 5). In Test Examples 1 and 2, hydrochloric acid was not mixed.
Next, the acid-treated product obtained by subjecting the acid treatment is filtered using a filter press device 9, the liquid phase is removed from the acid-treated product, the acid-treated product is filtered off, and the acid-treated product is filtered. Press cake 21 was obtained. The press cake 21 was dried under predetermined conditions to obtain a dried product (titanium hydroxide) of the press cake 21. The conditions for synthesizing the dried product (titanium hydroxide) of the press cake 21 from the aggregated press cake are as shown in Table 2. Further, the dried product (titanium hydroxide) of the obtained press cake 21 was subjected to an ICP emission spectroscopic analysis method (Inductive coupled plasma optical spectrum spectrum; ICP-OES) and contained chlorine (Cl) and calcium (Ca). The results of the measurement are also shown in Table 2.

Figure 0006959471
Figure 0006959471

表2に示した通り、希釈時の水と塩酸の添加量を調製して酸処理時の液相のpHを5.9以下にすることで、塩素とカルシウムの含量を低減可能なことが確認できた。 As shown in Table 2, it was confirmed that the chlorine and calcium contents can be reduced by adjusting the addition amount of water and hydrochloric acid at the time of dilution and lowering the pH of the liquid phase at the time of acid treatment to 5.9 or less. did it.

(実施例2)
<酸化チタンの合成>
図6に示す処理フローを用いて、チタン化合物を含む排液から酸化チタンを得た。
すなわち、チーグラーナッタ触媒の製造工場において、オレフィン類重合用固体触媒成分を調製した際に発生する、四塩化チタン、ジエトキシマグネシウム、トルエンおよびヘプタンを含む液温25℃の排液を処理対象とし、当該排液Dを容量250mの受水槽1に送入することで混合し、加水分解を施した。このとき、受水槽中の排液のpHが1になるように受水槽中に加水分解用の水11を送入した。
上記加水分解処理された処理液を、10m/hの速度で容量10mの一次中和処理槽2に送入し、液温25℃の12.5mol/L水酸化ナトリウム水溶液を用いて、一次中和処理槽2内に送入された処理液のpHが2.0になるように一次中和処理を施した。
次いで、上記一次中和処理を施した処理液を、10m/hの速度で容量10mの二次中和処理槽3に送入し、液温25℃の12.5mol/L水酸化カルシウム水溶液を用いて、二次中和処理槽3内に送入された処理液のpHが7.2になるように二次中和処理を施した。
二次中和処理を施した液温25℃の処理液は、10m/hの速度で容量10mの凝集槽4内に送入して、凝集剤(クリタ・ケミカル北陸(株)製クリファームPA−833)を用いて凝集させて凝集処理液を得た後、該凝集処理液を、沈降槽5に移送し、沈降槽5内で沈降させて、沈降槽5から沈降物を抜き出した。次いで、沈降槽5から抜き出した沈降物4000kgを、酸処理槽18に移送し、酸処理槽18に塩酸14を供給して、該沈降物と塩酸14を混合し、酸処理槽18内の液相のpHが3.5になるように酸処理を施した。次いで、得られた該凝集物の酸処理物を、フィルタープレス装置7を用いてろ過し、該凝集物の酸処理物から液相を除去して、該凝集物の酸処理物をろ別することにより、該凝集物の酸処理物のプレスケーキを得た。次いで、得られた該凝集物の酸処理物のプレスケーキを、洗浄槽32に移送し、洗浄槽槽32に洗浄水15を4000kg供給して、水酸化チタンの凝集物の酸処理物と洗浄水15を混合し、洗浄を行った。次いで、得られた該凝集物の酸処理物の洗浄物を、フィルタープレス装置33を用いてろ過し、該凝集物の酸処理物の洗浄物から液相を除去して、該凝集物の酸処理物をろ別することにより、該凝集物の酸処理物のプレスケーキ25を得た。該プレスケーキ25を、熱風循環乾燥機を用いて180℃、16時間の条件で乾燥し、プレスケーキ25の乾燥物(水酸化チタン)を得た。次いで、得られたプレスケーキ25の乾燥物(水酸化チタン)を、シャトルキルンを用いて大気雰囲気中で850℃、2時間加熱処理を施した後、950℃、2時間さらに加熱処理を施して、目的とする酸化チタンを得た。
得られた水酸化チタンおよび酸化チタンの結晶構造を、X’PERT−PRO−MPD多目的X線回析装置(PANalytical製)を用いて測定したところ、得られた水酸化チタンは少量のルチル型の酸化チタンを含むが主たる結晶系が非晶質であるのに対し、酸化チタンはルチル型であることが確認できた。
(Example 2)
<Synthesis of titanium oxide>
Using the treatment flow shown in FIG. 6, titanium oxide was obtained from the effluent containing a titanium compound.
That is, the wastewater containing titanium tetrachloride, diethoxymagnesium, toluene and heptane, which is generated when the solid catalyst component for olefin polymerization is prepared in the Ziegler-Natta catalyst manufacturing plant, is treated. The drainage D was mixed by feeding it into a water receiving tank 1 having a capacity of 250 m 3, and hydrolyzed. At this time, water 11 for hydrolysis was sent into the water receiving tank so that the pH of the drainage liquid in the water receiving tank became 1.
The hydrolyzed treatment liquid was fed into a primary neutralization treatment tank 2 having a capacity of 10 m 3 at a rate of 10 m 3 / h, and a 12.5 mol / L sodium hydroxide aqueous solution having a liquid temperature of 25 ° C. was used. The primary neutralization treatment was performed so that the pH of the treatment liquid fed into the primary neutralization treatment tank 2 became 2.0.
Next, the treatment liquid subjected to the above primary neutralization treatment was fed into the secondary neutralization treatment tank 3 having a capacity of 10 m 3 at a rate of 10 m 3 / h, and 12.5 mol / L calcium hydroxide having a liquid temperature of 25 ° C. Using an aqueous solution, the secondary neutralization treatment was performed so that the pH of the treatment liquid fed into the secondary neutralization treatment tank 3 became 7.2.
The treated liquid having been subjected to the secondary neutralization treatment and having a liquid temperature of 25 ° C. is fed into the coagulation tank 4 having a capacity of 10 m 3 at a speed of 10 m 3 / h, and is used as a coagulant (Kurita Chemical Hokuriku Co., Ltd. After aggregating using the farm PA-833) to obtain a coagulation treatment liquid, the coagulation treatment liquid was transferred to the settling tank 5 and settled in the settling tank 5, and the settling material was extracted from the settling tank 5. .. Next, 4000 kg of the sediment extracted from the sedimentation tank 5 is transferred to the acid treatment tank 18, hydrochloric acid 14 is supplied to the acid treatment tank 18, the sediment and hydrochloric acid 14 are mixed, and the liquid in the acid treatment tank 18 is liquid. Acid treatment was performed so that the pH of the phase became 3.5. Next, the acid-treated product of the obtained agglomerates is filtered using a filter press device 7, the liquid phase is removed from the acid-treated product of the agglomerates, and the acid-treated product of the agglomerates is filtered. As a result, a press cake of an acid-treated product of the aggregate was obtained. Next, the obtained press cake of the acid-treated product of the agglomerates is transferred to the washing tank 32, and 4000 kg of washing water 15 is supplied to the washing tank 32 to wash with the acid-treated product of the titanium hydroxide agglomerates. Water 15 was mixed and washed. Next, the obtained washed product of the acid-treated product of the aggregate is filtered using the filter press device 33, the liquid phase is removed from the washed product of the acid-treated product of the aggregate, and the acid of the aggregate is removed. By filtering the treated product, a press cake 25 of the acid-treated product of the aggregate was obtained. The press cake 25 was dried using a hot air circulation dryer at 180 ° C. for 16 hours to obtain a dried product (titanium hydroxide) of the press cake 25. Next, the dried product (titanium hydroxide) of the obtained press cake 25 was heat-treated at 850 ° C. for 2 hours in an air atmosphere using a shuttle kiln, and then further heat-treated at 950 ° C. for 2 hours. , The target titanium oxide was obtained.
When the crystal structures of the obtained titanium hydroxide and titanium oxide were measured using an X'PERT-PRO-MPD multipurpose X-ray diffractometer (manufactured by PANICAL), the obtained titanium hydroxide was of a rutile type in a small amount. It was confirmed that titanium oxide is a rutile type, whereas titanium oxide is contained but the main crystal system is amorphous.

<チタン酸カリウムの合成>
得られた酸化チタン52.16kgと、チタン鉱石52.23kg炭酸カリウム粉末32.28kg、チタン粉末2.87kgおよび、木屑(木質ペレット)5.70kgを、振動ロッドミル(中央化工機株式会社製)中に充填し、さらにここに低級アルコールを0.6kg添加して、振幅5mmで15分間処理することにより、原料混合物を得た。
上記の原料混合物おおよそ140kgを、温度1170℃のロータリーキルンへ14.4kg/hrの流量で供給した。このロータリーキルン内でチタン酸カリウムへの合成反応が起こり、焼成物となってロータリーキルンから排出された。排出された焼成物を室温まで急冷した。
その後、冷却した焼成物を振動ロッドミル(中央化工機株式会社製)で粉砕した後、分級機を内蔵した衝撃式粉砕機(ホソカワミクロン株式会社製、ACMパルベライザ)で粉砕し、チタン酸カリウム粒子を得た。得られたチタン酸カリウム粒子の各物性を表3に示す。また、走査型電子顕微鏡観察結果(SEM)を図10に示す。
なお、比較のため、表3には市販のチタン酸カリウム粒子(東邦チタニウム株式会社製、TOFIX−SNR−S)の各物性も示した。また、走査型電子顕微鏡観察結果(SEM)を図11に示す。
各物性の測定に用いた測定装置又は測定方法は以下の通りである。
≪測定装置≫
XRD:X’PERT−PRO−MPD多目的X線回析装置(PANalytical製)
SEM:JSM−7800(日本電子製)
比表面積:monosorb(quantacrome社製)
平均粒径:PITA−3(株式会社セイシン企業製)
<Synthesis of potassium titanate>
52.16 kg of the obtained titanium oxide, 52.23 kg of titanium ore, 32.28 kg of potassium carbonate powder, 2.87 kg of titanium powder, and 5.70 kg of wood chips (wood pellets) were placed in a vibrating rod mill (manufactured by Chuo Kakoki Co., Ltd.). Was filled with, and 0.6 kg of lower alcohol was further added thereto, and the mixture was treated with an amplitude of 5 mm for 15 minutes to obtain a raw material mixture.
Approximately 140 kg of the above raw material mixture was supplied to a rotary kiln at a temperature of 1170 ° C. at a flow rate of 14.4 kg / hr. A synthetic reaction to potassium titanate occurred in this rotary kiln, and it became a fired product and was discharged from the rotary kiln. The discharged fired product was rapidly cooled to room temperature.
After that, the cooled calcined product was crushed with a vibrating rod mill (manufactured by Chuo Kakoki Co., Ltd.) and then crushed with an impact type crusher (manufactured by Hosokawa Micron Co., Ltd., ACM Pulverizer) with a built-in classifier to obtain potassium titanate particles. rice field. Table 3 shows the physical characteristics of the obtained potassium titanate particles. The scanning electron microscope observation result (SEM) is shown in FIG.
For comparison, Table 3 also shows the physical characteristics of commercially available potassium titanate particles (TOFIX-SNR-S manufactured by Toho Titanium Co., Ltd.). The scanning electron microscope observation result (SEM) is shown in FIG.
The measuring device or measuring method used for measuring each physical property is as follows.
≪Measuring device≫
XRD: X'PERT-PRO-MPD multipurpose X-ray diffractometer (manufactured by PANalytical)
SEM: JSM-7800 (manufactured by JEOL Ltd.)
Specific surface area: monosorb (manufactured by quantachrome)
Average particle size: PITA-3 (manufactured by Seishin Enterprise Co., Ltd.)

Figure 0006959471
1)6KTO:6チタン酸カリウム
Figure 0006959471
1) 6KTO: Potassium 6 titanate

表3に示した通り、実施例2のチタン酸カリウム粒子は、市販品と比較して、同じ相構成及び粉末形状を有していることが確認できた。また、比表面積(規格値:2〜3m/g)、平均粒径(規格値:25〜60μm)についても、市販品の規格値内であった。 As shown in Table 3, it was confirmed that the potassium titanate particles of Example 2 had the same phase composition and powder shape as those of the commercially available product. The specific surface area (standard value: 2 to 3 m 2 / g) and average particle size (standard value: 25 to 60 μm) were also within the standard values of commercially available products.

(試験例6〜試験例8)
実施例2と同様にして得られた沈降槽5から抜き出した沈降物を、酸処理槽18に移送し、酸処理槽18に塩酸14を供給して、所定時間撹拌して該沈降物と塩酸14を混合し、酸処理槽18内の混合液のpHが表4の所定値になるように酸処理を施した(試験例7〜8)。なお、試験例6では、塩酸を混合しなかった。
次いで、得られた該凝集物の酸処理物を、フィルタープレス装置7を用いてろ過し、該凝集物の酸処理物から液相を除去して、該凝集物の酸処理物をろ別することにより、該凝集物の酸処理物のプレスケーキを得た。該プレスケーキを、所定条件で乾燥し、プレスケーキの乾燥物(水酸化チタン)を得た。なお、沈降槽5から抜き出した沈降物からプレスケーキの乾燥物(水酸化チタン)を合成するための各条件は、表4に示した通りである。また、得られたプレスケーキの乾燥物(水酸化チタン)について、ICP発光分光分析法(Inductivity coupled plasma optical emission spectrometer;ICP−OES)を用い、カルシウム(Ca)の含有量を測定した結果もあわせて表4に示した。
(Test Example 6 to Test Example 8)
The sediment extracted from the sedimentation tank 5 obtained in the same manner as in Example 2 is transferred to the acid treatment tank 18, hydrochloric acid 14 is supplied to the acid treatment tank 18, and the sediment and hydrochloric acid are stirred for a predetermined time. 14 was mixed, and acid treatment was performed so that the pH of the mixed solution in the acid treatment tank 18 became the predetermined value in Table 4 (Test Examples 7 to 8). In Test Example 6, hydrochloric acid was not mixed.
Next, the acid-treated product of the obtained agglomerates is filtered using a filter press device 7, the liquid phase is removed from the acid-treated product of the agglomerates, and the acid-treated product of the agglomerates is filtered. As a result, a press cake of an acid-treated product of the aggregate was obtained. The press cake was dried under predetermined conditions to obtain a dried product (titanium hydroxide) of the press cake. The conditions for synthesizing the dried product (titanium hydroxide) of the press cake from the sediment extracted from the sedimentation tank 5 are as shown in Table 4. In addition, the results of measuring the calcium (Ca) content of the obtained dried product (titanium hydroxide) using ICP emission spectrometry (ICP-OES) are also included. It is shown in Table 4.

Figure 0006959471
Figure 0006959471

表4に示した通り、希釈時の水と塩酸の添加量を調製して酸処理時の液相のpHを5.9以下にすることで、カルシウムの含量を低減可能なことが確認できた。 As shown in Table 4, it was confirmed that the calcium content can be reduced by adjusting the addition amounts of water and hydrochloric acid at the time of dilution and setting the pH of the liquid phase at the time of acid treatment to 5.9 or less. ..

表1及び表3より、実施例1〜実施例2においては、チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する加水分解処理を施した後、加水分解処理を施した排液の水相に対し、pHが1.5以上2.5未満になるように中和剤を加える一次中和処理を施し、次いで、一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤を加える二次中和処理を施して、次いで、水酸化チタンを凝集させて生じる水酸化チタンの凝集物に、pH5.9以下の塩酸を接触させることにより、アンモニア水や水酸化ナトリウム等の中和剤を用いなくても容易にチタン化合物が得られるとともに、チタン化合物としてカルシウム等の不純物の混入が抑制された高純度なものが得られることが分かる。 From Tables 1 and 3, in Examples 1 and 2, the effluent containing the titanium compound was brought into contact with water, and the titanium compound was subjected to the hydrolysis treatment and then the hydrolysis treatment. The aqueous phase of the effluent is subjected to a primary neutralization treatment in which a neutralizing agent is added so that the pH is 1.5 or more and less than 2.5. A secondary neutralization treatment is performed in which a neutralizing agent is added so as to be 6.5 or more and 7.5 or less, and then agglomerates of titanium hydroxide formed by aggregating titanium hydroxide are subjected to hydrochloric acid having a pH of 5.9 or less. A titanium compound can be easily obtained without using a neutralizing agent such as aqueous ammonia or sodium hydroxide, and a high-purity titanium compound in which impurities such as calcium are suppressed from being mixed can be obtained. It turns out that it can be done.

また、表2及び表4より、試験例4、試験例7及び試験例8においては、二次中和処理後の水酸化チタンを凝集させて生じる水酸化チタンの凝集物に、pH5.9以下の塩酸を接触させることにより、得られるチタン化合物中のカルシウム等の不純物が除去されることが分かる。
一方、試験例1〜3、5及び試験例6においては、二次中和処理後の水酸化チタンを凝集させて生じる水酸化チタンの凝集物に、pH5.9以下の塩酸を接触させていないことから、得られるチタン化合物中にカルシウム等の不純物が除去されないことが分かる。
Further, from Tables 2 and 4, in Test Example 4, Test Example 7 and Test Example 8, the pH of the titanium hydroxide agglomerates formed by aggregating the titanium hydroxide after the secondary neutralization treatment was pH 5.9 or less. It can be seen that impurities such as calcium in the obtained titanium compound are removed by contacting with hydrochloric acid.
On the other hand, in Test Examples 1 to 3 and 5 and Test Example 6, hydrochloric acid having a pH of 5.9 or less was not brought into contact with the aggregate of titanium hydroxide formed by agglutinating titanium hydroxide after the secondary neutralization treatment. From this, it can be seen that impurities such as calcium are not removed from the obtained titanium compound.

本発明によれば、チタン化合物を含有する排液、例えば、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタン化合物含有排液等のチタン化合物を含有する排液から、中和剤として水酸化カルシウム又は酸化カルシウムを用いても、チタン化合物を高純度で簡便に回収する方法を提供することができるとともに、チタン化合物を含有する排液、例えば、オレフィン類重合用固体触媒成分又はオレフィン類重合用触媒を調製する際に発生するチタン化合物含有排液等のチタン化合物を含有する排液から、中和剤として水酸化カルシウム又は酸化カルシウムを用いても、チタン化合物を高純度で簡便に製造する方法を提供することができ、さらに、高純度なチタン酸アルカリ金属を低コストに製造する方法を提供することができる。 According to the present invention, a effluent containing a titanium compound, for example, a effluent containing a titanium compound such as a solid catalyst component for olefin polymerization or a titanium compound-containing effluent generated when a catalyst for olefin polymerization is prepared. Therefore, even if calcium hydroxide or calcium oxide is used as the neutralizing agent, it is possible to provide a method for easily recovering the titanium compound with high purity, and for effluent containing the titanium compound, for example, for olefin polymerization. Even if calcium hydroxide or calcium oxide is used as a neutralizing agent from the effluent containing a titanium compound such as the effluent containing a titanium compound generated when preparing a solid catalyst component or a catalyst for olefin polymerization, the titanium compound can be obtained. It is possible to provide a method for producing a high-purity and simple method, and further, it is possible to provide a method for producing a high-purity alkali metal titanate at low cost.

1 受水槽
2 一次中和処理槽
3 二次中和処理槽
4 凝集槽
5 沈殿槽
6 沈殿物貯蔵槽
7、9、33 フィルタープレス装置
8、18 酸処理槽
10 チタン化合物を含む排液
11 水
12、13 水酸化カルシウム懸濁液
14 塩酸
15 洗浄水
19 水酸化チタン化合物の凝集物
20 水酸化チタン化合物の凝集物の酸処理物
21、22、23、24、25、26 水酸化チタン化合物の凝集物の酸処理物のプレスケーキ
31、32 洗浄槽
1 Water receiving tank 2 Primary neutralization treatment tank 3 Secondary neutralization treatment tank 4 Coagulation tank 5 Sedimentation tank 6 Sediment storage tanks 7, 9, 33 Filter press devices 8, 18 Acid treatment tank 10 Drainage containing titanium compounds 11 Water 12, 13 Calcium hydroxide suspension 14 Hydrochloride 15 Washing water 19 Titanium hydroxide compound agglomerates 20 Acid-treated products of titanium hydroxide compound agglomerates 21, 22, 23, 24, 25, 26 Titanium hydroxide compounds Acid-treated agglomerates Press cake 31, 32 Washing tank

Claims (13)

チタン化合物を含む排液からチタン成分を回収するチタン成分の回収方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3)と、
を有すること、
を特徴とするチタン成分の回収方法。
A method for recovering a titanium component from a effluent containing a titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. Step (2) to obtain agglomerates of titanium hydroxide by performing agglomeration treatment
In the step after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the titanium hydroxide agglutination to obtain an acid-treated product of the titanium hydroxide agglutination.
To have
A method for recovering a titanium component, which is characterized by.
前記工程(2)を行い生じる前記水酸化チタンの凝集物の濃縮物を得た後、該水酸化チタンの凝集物の濃縮物を分離し、次いで、該水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、前記水酸化チタンの凝集物の酸処理物を得る工程(3A)を有することを特徴とする請求項1記載のチタン成分の回収方法。 After obtaining the concentrate of the titanium hydroxide agglomerate produced by performing the step (2), the concentrate of the titanium hydroxide agglomerate is separated, and then the concentrate of the titanium hydroxide agglomerate is obtained. The titanium according to claim 1, further comprising a step (3A) of contacting with hydrochloric acid to perform acid treatment of the titanium hydroxide agglomerate to obtain an acid-treated product of the titanium hydroxide agglomerate. How to recover the ingredients. 前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させることにより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする請求項2記載のチタン成分の回収方法。 The second aspect of the present invention, wherein in the step (3A), a concentrate of the titanium hydroxide agglomerates is obtained by precipitating the titanium hydroxide agglomerates produced by performing the step (2). How to recover the titanium component. 前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物を分離し、次いで、該水酸化チタンの凝集物の沈降物から液相を除去する脱水処理を行い、水酸化チタンの凝集物の脱水処理物を得ることより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする請求項2記載のチタン成分の回収方法。 In the step (3A), after the agglomerates of the titanium hydroxide produced by performing the step (2) are settled, the agglomerates of the titanium hydroxide are separated, and then the agglomerates of the titanium hydroxide are separated. 2. The invention according to claim 2, wherein a dehydration treatment for removing the liquid phase from the precipitate of titanium hydroxide is performed to obtain a dehydrated product of the agglomerates of titanium hydroxide, thereby obtaining a concentrate of the agglomerates of titanium hydroxide. How to recover the titanium component of. 前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3B)を有することを特徴とする請求項1記載のチタン成分の回収方法。 After the titanium hydroxide agglomerates produced by performing the step (2) are settled, hydrochloric acid is brought into contact with the titanium hydroxide agglomerates to carry out acid treatment of the titanium hydroxide agglomerates. The method for recovering a titanium component according to claim 1, further comprising a step (3B) of obtaining an acid-treated product of agglomerates of titanium hydroxide. 前記水酸化チタンの凝集物の酸処理物を、6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することを特徴とする請求項1〜5いずれか1項記載のチタン成分の回収方法。 The titanium component according to any one of claims 1 to 5, further comprising a washing step of washing the acid-treated product of the titanium hydroxide agglomerate with washing water of 6.0 or more and 9.0 or less. Collection method. チタン化合物を含む排液から酸化チタンを製造する酸化チタンの製造方法であって、
該チタン化合物を含む排液を水と接触させ、チタン化合物を加水分解処理する工程(1)と、
加水分解処理を施した処理液に対し、pHが1.5以上2.5未満になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える一次中和処理を施し、次いで、該一次中和処理を施した処理液に対し、pHが6.5以上7.5以下になるように中和剤として水酸化カルシウム又は酸化カルシウムを加える二次中和処理を施し、次いで、水酸化チタンを凝集させる凝集処理を行い、水酸化チタンの凝集物を得る工程(2)と、
該工程(2)より後段において、該水酸化チタンの凝集物に塩酸を接触させる酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3)と、
該水酸化チタンの凝集物の酸処理物を酸化して、酸化チタンを得る酸化工程と、
を有すること、
を特徴とする酸化チタンの製造方法。
A method for producing titanium oxide from a effluent containing a titanium compound.
The step (1) of hydrolyzing the titanium compound by bringing the effluent containing the titanium compound into contact with water.
The hydrolyzed treatment liquid is subjected to a primary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH is 1.5 or more and less than 2.5, and then the primary neutralization is performed. The treated liquid is subjected to a secondary neutralization treatment in which calcium hydroxide or calcium oxide is added as a neutralizing agent so that the pH becomes 6.5 or more and 7.5 or less, and then titanium hydroxide is aggregated. Step (2) to obtain agglomerates of titanium hydroxide by performing agglomeration treatment
In the step after the step (2), an acid treatment is performed in which hydrochloric acid is brought into contact with the titanium hydroxide agglutination to obtain an acid-treated product of the titanium hydroxide agglutination.
An oxidation step of oxidizing the acid-treated product of the titanium hydroxide agglomerate to obtain titanium oxide, and
To have
A method for producing titanium oxide.
前記工程(2)を行い生じる前記水酸化チタンの凝集物の濃縮物を得た後、該水酸化チタンの凝集物の濃縮物を分離し、次いで、該水酸化チタンの凝集物の濃縮物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、前記水酸化チタンの凝集物の酸処理物を得る工程(3A)を有することを特徴とする請求項7記載のチタン成分の回収方法。 After obtaining the concentrate of the titanium hydroxide agglomerate produced by performing the step (2), the concentrate of the titanium hydroxide agglomerate is separated, and then the concentrate of the titanium hydroxide agglomerate is obtained. The titanium according to claim 7, further comprising a step (3A) of contacting with hydrochloric acid to perform acid treatment of the titanium hydroxide agglomerate to obtain an acid-treated product of the titanium hydroxide agglomerate. How to recover the ingredients. 前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させることにより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする請求項8記載のチタン成分の回収方法。 The eighth aspect of the present invention, wherein in the step (3A), a concentrate of the titanium hydroxide agglomerates is obtained by precipitating the titanium hydroxide agglomerates produced by performing the step (2). How to recover the titanium component. 前記工程(3A)において、前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物を分離し、次いで、該水酸化チタンの凝集物の沈降物から液相を除去する脱水処理を行い、水酸化チタンの凝集物の脱水処理物を得ることより、前記水酸化チタンの凝集物の濃縮物を得ることを特徴とする請求項8記載のチタン成分の回収方法。 In the step (3A), after the agglomerates of the titanium hydroxide produced by performing the step (2) are settled, the agglomerates of the titanium hydroxide are separated, and then the agglomerates of the titanium hydroxide are separated. 8. The eighth aspect of claim 8, wherein a dehydration treatment for removing the liquid phase from the precipitate of titanium hydroxide is performed to obtain a dehydrated product of the agglomerates of titanium hydroxide, thereby obtaining a concentrate of the agglomerates of titanium hydroxide. How to recover the titanium component of. 前記工程(2)を行い生じる前記水酸化チタンの凝集物を沈降させた後、水酸化チタンの凝集物の沈降物に、塩酸を接触させて、該水酸化チタンの凝集物の酸処理を行い、水酸化チタンの凝集物の酸処理物を得る工程(3B)を有することを特徴とする請求項7記載の酸化チタンの製造方法。 After the titanium hydroxide agglomerates produced by performing the step (2) are precipitated, hydrochloric acid is brought into contact with the titanium hydroxide agglomerates to carry out acid treatment of the titanium hydroxide agglomerates. The method for producing titanium oxide according to claim 7, further comprising a step (3B) of obtaining an acid-treated product of agglomerates of titanium hydroxide. 前記水酸化チタンの凝集物の酸処理物を、6.0以上9.0以下の洗浄水で洗浄する洗浄工程を有することを特徴とする請求項7〜11いずれか1項記載の酸化チタンの製造方法。 The titanium oxide according to any one of claims 7 to 11, further comprising a washing step of washing the acid-treated product of the aggregate of titanium hydroxide with washing water of 6.0 or more and 9.0 or less. Production method. 請求項1〜6いずれか1項記載のチタン成分の回収方法により回収された水酸化チタン、又は請求項7〜12いずれか1項記載の酸化チタンの製造方法により得られた酸化チタンを原料として用いることを特徴とするチタン酸アルカリ金属の製造方法。 Using titanium hydroxide recovered by the method for recovering the titanium component according to any one of claims 1 to 6 or titanium oxide obtained by the method for producing titanium oxide according to any one of claims 7 to 12 as a raw material. A method for producing an alkali metal titanate, which is characterized by being used.
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Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103031440A (en) * 2011-10-09 2013-04-10 中国石油化工股份有限公司 Treatment method of titanium-containing waste liquid
JP2018080086A (en) * 2016-11-17 2018-05-24 東邦チタニウム株式会社 Method for recovering titanium compound, method for producing titanium oxide, and method for producing alkali titanate
JP2019196278A (en) * 2018-05-08 2019-11-14 東邦チタニウム株式会社 Method for recovering titanium compound, method for producing titanium oxide, and method for producing alkali titanate

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103031440A (en) * 2011-10-09 2013-04-10 中国石油化工股份有限公司 Treatment method of titanium-containing waste liquid
JP2018080086A (en) * 2016-11-17 2018-05-24 東邦チタニウム株式会社 Method for recovering titanium compound, method for producing titanium oxide, and method for producing alkali titanate
JP2019196278A (en) * 2018-05-08 2019-11-14 東邦チタニウム株式会社 Method for recovering titanium compound, method for producing titanium oxide, and method for producing alkali titanate

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