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JP5160215B2 - Method for treating sodium hydroxide waste solution of aluminum material - Google Patents
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JP5160215B2 - Method for treating sodium hydroxide waste solution of aluminum material - Google Patents

Method for treating sodium hydroxide waste solution of aluminum material Download PDF

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JP5160215B2
JP5160215B2 JP2007335730A JP2007335730A JP5160215B2 JP 5160215 B2 JP5160215 B2 JP 5160215B2 JP 2007335730 A JP2007335730 A JP 2007335730A JP 2007335730 A JP2007335730 A JP 2007335730A JP 5160215 B2 JP5160215 B2 JP 5160215B2
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aluminum
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sodium hydroxide
carbon dioxide
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徹 福永
倫之 中村
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Unix Co Ltd
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本発明は、アルミニウム材を水酸化ナトリウム溶液でエッチングすることによって生じるアルミニウム材の水酸化ナトリウム処理廃液の処理方法及びアルミニウム材の水酸化ナトリウム処理廃液由来産物の製造方法に関する。さらに詳しくは、水酸化ナトリウム溶液でアルミニウム材をエッチングした後、硫酸溶液中でアルミニウム材に陽極酸化被膜を形成させる、アルミニウム材の表面処理工程で生じるエッチング廃液の処理に好適なものである。   The present invention relates to a method for treating a sodium hydroxide treatment waste liquid of an aluminum material produced by etching an aluminum material with a sodium hydroxide solution and a method for producing a product derived from a sodium hydroxide treatment waste liquid of an aluminum material. More specifically, the present invention is suitable for treatment of an etching waste liquid generated in a surface treatment process of an aluminum material, in which an aluminum material is etched with a sodium hydroxide solution and then an anodized film is formed on the aluminum material in a sulfuric acid solution.

アルミニウムサッシ等の建材やその他アルミニウム工業材料等のアルミニウム材は、例えば、耐久性を高めるため、前処理として水酸化ナトリウム溶液によりエッチングが行われ、続いて硫酸溶液中で電解酸化させ、表面に陽極酸化被膜を形成させることが行われている。この水酸化ナトリウム溶液によるエッチングでは、アルミニウム材の表面が、水酸化ナトリウム溶液に溶解してアルミン酸ソーダが生成し、徐々にエッチング液中のアルミン酸ソーダ濃度が高くなってくる。エッチング液のエッチング能力は、アルミン酸ソーダ濃度が高くなるに伴って低下するため、ある程度アルミン酸ソーダ濃度が高まった時点で新しいエッチング液に交換する必要がある。
エッチング廃液を、アルミニウムをエッチング可能な水酸化ナトリウム溶液として再生する方法の例として、下記特許文献1、2に示されるような、(1)アルミン酸ソーダが過飽和となってしまったエッチング廃液中のアルミン酸ソーダを加水分解し、(2)水酸化アルミニウムを析出させ、(3)析出した水酸化アルミニウムを濾過分離し、(4)濾液に水酸化ナトリウムを加え濃度調整をする、ことによってエッチング廃液を再生するという方法が知られている。
特開昭48−38890号公報 特開平05−279020号公報
Aluminum materials such as building materials such as aluminum sashes and other aluminum industrial materials, for example, are etched with a sodium hydroxide solution as a pretreatment, and then electrolytically oxidized in a sulfuric acid solution to increase durability, and an anode is formed on the surface. An oxide film is formed. In the etching with the sodium hydroxide solution, the surface of the aluminum material is dissolved in the sodium hydroxide solution to produce sodium aluminate, and the concentration of sodium aluminate in the etching solution gradually increases. Since the etching ability of the etching solution decreases as the sodium aluminate concentration increases, it is necessary to replace the etching solution with a new etching solution when the sodium aluminate concentration increases to some extent.
As an example of a method for regenerating an etching waste liquid as a sodium hydroxide solution capable of etching aluminum, as shown in Patent Documents 1 and 2 below, (1) in an etching waste liquid in which sodium aluminate is supersaturated Etching waste liquid by hydrolyzing sodium aluminate, (2) precipitating aluminum hydroxide, (3) separating the precipitated aluminum hydroxide by filtration, and (4) adjusting the concentration by adding sodium hydroxide to the filtrate. The method of reproducing | regenerating is known.
JP-A-48-38890 Japanese Patent Laid-Open No. 05-279020

しかしながら、エッチング廃液中のアルミン酸ソーダを水酸化アルミニウムに加水分解するには、エッチング廃液中に水酸化アルミニウムの種子を核として投入し、晶析反応層で液温を40℃から60℃に保ちながら、40時間から70時間という長時間に亘って撹拌し続けなければならない。このため、大量のエッチング廃液を処理するためには、必然的に設備の規模が大きくなってしまい、ランニングコストが増大してしまうという問題があった。
そこで、本発明の主たる課題は、短時間且つ低コストでエッチング廃液から水酸化アルミニウムを分離回収することのできるアルミニウム材の水酸化ナトリウム処理廃液の処理方法を提供することにある。
However, in order to hydrolyze sodium aluminate in the etching waste liquid to aluminum hydroxide, aluminum hydroxide seeds are introduced into the etching waste liquid as a core, and the liquid temperature is maintained at 40 to 60 ° C. in the crystallization reaction layer. However, stirring must be continued for a long period of 40 to 70 hours. For this reason, in order to process a large amount of etching waste liquid, there was a problem that the scale of the facility inevitably increased and the running cost increased.
Therefore, a main problem of the present invention is to provide a method for treating a sodium hydroxide treatment waste liquid of aluminum material that can separate and recover aluminum hydroxide from an etching waste liquid in a short time and at a low cost.

上記課題を解決した本発明は次記のとおりである。
<請求項1記載の発明>
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法によりポリ塩化アルミニウムを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。
(1)前記水酸化ナトリウム処理廃液に、液温が50℃〜80℃の状態で、炭酸ガスを吹き込み、
析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、
(2)前記水酸化アルミニウムの全部または一部を塩酸に加えてスラリー化し、加圧加熱条件下で反応させ、反応スラリーを得る工程、
(3)前記反応スラリーに前記炭酸ソーダの一部を添加して反応させ、濾過により濾液を得る工程、及び
(4)前記濾液に硫酸ソーダを添加して反応させ、濾過により濾液としてポリ塩化アルミニウムを得る工程。
The present invention that has solved the above problems is as follows.
<Invention of Claim 1>
An aluminum characterized in that polyaluminum chloride is produced from a sodium hydroxide treatment waste solution of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of waste aluminum hydroxide treatment liquid.
(1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid in a state where the liquid temperature is 50 ° C. to 80 ° C.,
The precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is in solution or as a solid by drying,
(2) adding all or part of the aluminum hydroxide to hydrochloric acid to form a slurry and reacting under pressure and heating conditions to obtain a reaction slurry;
(3) A step of adding a part of the sodium carbonate to the reaction slurry for reaction, and obtaining a filtrate by filtration; and (4) adding sodium sulfate to the filtrate for reaction, and filtering to form polyaluminum chloride as a filtrate. Obtaining.

<請求項2記載の発明>
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法により硫酸バンドを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。
(1)前記水酸化ナトリウム処理廃液に、液温が50℃〜80℃の状態で、炭酸ガスを吹き込み、
析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、
(2)前記水酸化アルミニウムの全部または一部に硫酸を加え、空気撹拌により反応スラリーを得る工程、
(3)前記反応スラリーに水を加えて濃度を調整した後、濾過により濾液として硫酸バンドを得る工程。
<Invention of Claim 2>
An aluminum material characterized in that a sulfuric acid band is produced from a sodium hydroxide treatment waste liquid of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of aluminum hydroxide waste liquid.
(1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid in a state where the liquid temperature is 50 ° C. to 80 ° C.,
The precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is in solution or as a solid by drying,
(2) adding sulfuric acid to all or a part of the aluminum hydroxide and obtaining a reaction slurry by stirring with air;
(3) A step of adjusting the concentration by adding water to the reaction slurry and then obtaining a sulfate band as a filtrate by filtration.

<請求項3記載の発明>
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法によりポリ塩化アルミニウムを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。
(1)前記水酸化ナトリウム処理廃液に、液温が30℃〜40℃で、炭酸ガスを吹き込むことにより、遊離水酸化ナトリウム分を炭酸ソーダ化して析出させ濾過分離し、
他方、濾液に、液温が50℃〜80℃で、炭酸ガスを吹き込み、析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、
(2)前記水酸化アルミニウムの全部または一部を塩酸に加えてスラリー化し、加圧加熱条件下で反応させ、反応スラリーを得る工程、
(3)前記反応スラリーに前記炭酸ソーダの一部を添加して反応させ、濾過により濾液を得る工程、及び
(4)前記濾液に硫酸ソーダを添加して反応させ、濾過により濾液としてポリ塩化アルミニウムを得る工程。
<Invention of Claim 3>
An aluminum characterized in that polyaluminum chloride is produced from a sodium hydroxide treatment waste solution of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of waste aluminum hydroxide treatment liquid.
(1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid at a temperature of 30 ° C. to 40 ° C., so that free sodium hydroxide is converted to sodium carbonate, precipitated, separated by filtration,
On the other hand, carbon dioxide is blown into the filtrate at a temperature of 50 ° C. to 80 ° C., and the precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is or as a solid by drying. Process,
(2) adding all or part of the aluminum hydroxide to hydrochloric acid to form a slurry and reacting under pressure and heating conditions to obtain a reaction slurry;
(3) adding a part of the sodium carbonate to the reaction slurry to cause reaction, and obtaining a filtrate by filtration; and
(4) A step of adding sodium sulfate to the filtrate to cause reaction, and obtaining polyaluminum chloride as a filtrate by filtration.

<請求項4記載の発明>
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法により硫酸バンドを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。
(1)前記水酸化ナトリウム処理廃液に、液温が30℃〜40℃で、炭酸ガスを吹き込むことにより、遊離水酸化ナトリウム分を炭酸ソーダ化して析出させ濾過分離し、
他方、濾液に、液温が50℃〜80℃で、炭酸ガスを吹き込み、析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、
(2)前記水酸化アルミニウムの全部または一部に硫酸を加え、空気撹拌により反応スラリーを得る工程、
(3)前記反応スラリーに水を加えて濃度を調整した後、濾過により濾液として硫酸バンドを得る工程。
<Invention of Claim 4>
An aluminum material characterized in that a sulfuric acid band is produced from a sodium hydroxide treatment waste liquid of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of aluminum hydroxide waste liquid.
(1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid at a temperature of 30 ° C. to 40 ° C., so that free sodium hydroxide is converted to sodium carbonate, precipitated, separated by filtration,
On the other hand, carbon dioxide is blown into the filtrate at a temperature of 50 ° C. to 80 ° C., and the precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is or as a solid by drying. Process,
(2) adding sulfuric acid to all or a part of the aluminum hydroxide and obtaining a reaction slurry by stirring with air;
(3) A step of adjusting the concentration by adding water to the reaction slurry and then obtaining a sulfate band as a filtrate by filtration.

<請求項5記載の発明>
炭酸ガスは、ボイラーの燃焼排ガス、発酵排ガス、石灰石の焙焼炉から発生する炭酸ガスを用いる、請求項1〜4のいずれか1項に記載のアルミニウム材の水酸化ナトリウム処理廃液の処理方法。
<Invention of Claim 5>
The carbon dioxide gas is a treatment method of a sodium hydroxide treatment waste liquid of an aluminum material according to any one of claims 1 to 4, wherein carbon dioxide gas generated from a combustion exhaust gas from a boiler, a fermentation exhaust gas, or a limestone roasting furnace is used.

(作用効果)
上記の課題を解決すべく調査した結果、本発明者等は、アルミニウム材の水酸化ナトリウム処理廃液中のアルミン酸ソーダに炭酸ガスを吹き込めば、水酸化アルミニウムを得ることができるのではないかと考え、これを実施したところ、簡易かつ短時間に水酸化アルミニウム及び炭酸ソーダに変化させて回収することができることを知見した。
本発明におけるアルミン酸ソーダに炭酸ガスを吹き込んで水酸化アルミニウムを得る反応式は下記のとおりであると考えられる。
NaAlO2+ 2H2O = Na[Al(OH)4]=Al(OH)3 + NaOH …(1)
2Na[Al(OH)4]+ CO2= 2Al(OH)3 + Na2CO3 + H2O …(2)
(1)式はアルミン酸ソーダの加水分解反応を示し、(2)式はアルミン酸ソーダと炭酸ガスの反応を示している。この式によれば、アルミニウム分は水酸化アルミニウムになりナトリウム分は炭酸ソーダになることがわかる。
2NaOH+ CO2 =Na2CO3 + H2O …(3)
また、エッチング廃液には多量の水酸化ナトリウムが残存しているが、この水酸化ナトリウムも(3)式より炭酸ガスと反応すると炭酸ソーダと水になる。これらのことから、アルミニウムを水酸化ナトリウムによりエッチングすることで生じる、多量のアルミン酸ソーダを含むエッチング廃液の処理に炭酸ガス吹き込みが有効である。さらに、得られる水酸化アルミニウムは水に不溶解であり、炭酸ソーダの水に対する溶解度は温度によって差がある。従って、この性質を利用すれば両者の分離は容易に行うことができる。
(Function and effect)
As a result of investigating to solve the above-mentioned problems, the present inventors think that aluminum hydroxide can be obtained by blowing carbon dioxide into sodium aluminate in the sodium hydroxide treatment waste liquid of aluminum material. When this was carried out, it was found that it can be recovered simply and in a short time by changing to aluminum hydroxide and sodium carbonate.
The reaction formula for obtaining aluminum hydroxide by blowing carbon dioxide into sodium aluminate in the present invention is considered as follows.
NaAlO 2 + 2H 2 O = Na [Al (OH) 4 ] = Al (OH) 3 + NaOH (1)
2Na [Al (OH) 4 ] + CO 2 = 2Al (OH) 3 + Na 2 CO 3 + H 2 O (2)
The formula (1) shows the hydrolysis reaction of sodium aluminate, and the formula (2) shows the reaction of sodium aluminate and carbon dioxide. According to this formula, it can be seen that the aluminum content is aluminum hydroxide and the sodium content is sodium carbonate.
2NaOH + CO 2 = Na 2 CO 3 + H 2 O ... (3)
In addition, a large amount of sodium hydroxide remains in the etching waste liquid, but this sodium hydroxide also becomes sodium carbonate and water when it reacts with carbon dioxide from the formula (3). From these, caused by etching the aluminum with sodium hydroxide, it is effective blowing of carbon dioxide gas into the process of etching waste liquid containing a large amount of sodium aluminate. Furthermore, the obtained aluminum hydroxide is insoluble in water, and the solubility of sodium carbonate in water varies with temperature . Therefore, if this property is utilized, both can be easily separated.

実際、本発明者等は試行的に、エッチング廃液の液温を15℃とし、撹拌しつつ炭酸ガスを吹き込んだところ、液温が反応熱によって徐々に上昇してきた。さらに炭酸ガスの吹き込みを続けると、白色の結晶が生成し始めた。エッチング廃液の液温が42℃になるとそれ以上液温が上昇しなくなったので、反応が終了したものと判断し炭酸ガスの吹き込みを停止して真空濾過器により固液分離した。   In fact, the inventors of the present invention trially set the liquid temperature of the etching waste liquid to 15 ° C. and blown carbon dioxide gas with stirring. As a result, the liquid temperature gradually increased due to reaction heat. When carbon dioxide was continuously blown, white crystals started to form. When the liquid temperature of the etching waste liquid reached 42 ° C., the liquid temperature did not rise any further. Therefore, it was judged that the reaction was completed, and blowing of carbon dioxide gas was stopped, and solid-liquid separation was performed using a vacuum filter.

本発明者等は、固液分離により得られた固体が水酸化アルミニウムと炭酸ソーダとの混合物であると考え、60℃の温水で洗浄することで炭酸ソーダ分を分離して純度の高い水酸化アルミニウムを得ようとしたところ、全量が溶解してしまった。この事実から、本発明者等は、生成した結晶は炭酸ソーダであり、エッチング廃液中のフリーの水酸化ナトリウムが炭酸ガスと反応して生じたもので、アルミン酸ソーダ中のナトリウムはフリーの水酸化ナトリウムが存在するうちは炭酸ガスと反応しにくく、そのため、本実験における液温の上昇が停止した42℃ではアルミン酸ソーダと炭酸ガスの反応は起きていなかったと推察した。   The present inventors consider that the solid obtained by solid-liquid separation is a mixture of aluminum hydroxide and sodium carbonate, and separate the sodium carbonate content by washing with hot water at 60 ° C. to obtain high-purity hydroxide. When trying to obtain aluminum, the whole amount was dissolved. From this fact, the present inventors have found that the generated crystals are sodium carbonate, and free sodium hydroxide in the etching waste liquid is produced by reacting with carbon dioxide, and sodium in sodium aluminate is free water. While sodium oxide was present, it was difficult to react with carbon dioxide, so it was assumed that the reaction between sodium aluminate and carbon dioxide did not occur at 42 ° C. when the rise in the liquid temperature in this experiment stopped.

そこで、真空濾過器による固液分離で得られた濾液の液温を60℃に保つようにウォーターバスで温度調節しつつ炭酸ガスを吹き込んだところ、再度結晶の生成が始まったので、充分炭酸ガスを吹き込んだ後濾過分離した。得られた固形物を60℃の温水で洗浄したところ純度の高い水酸化アルミニウムが生成したのが確認できた。本発明者等は、この実験を基に、さらなる調査及び実験を重ね、本発明を完成させるに至ったものである。   Therefore, when carbon dioxide gas was blown in while adjusting the temperature with a water bath so that the temperature of the filtrate obtained by solid-liquid separation with a vacuum filter was kept at 60 ° C., the formation of crystals started again, so carbon dioxide gas was sufficient. And then separated by filtration. When the obtained solid was washed with hot water at 60 ° C., it was confirmed that high-purity aluminum hydroxide was produced. The present inventors have made further investigations and experiments based on this experiment, and have completed the present invention.

本発明によれば、下記の実施例における実験結果にも示すとおり、従来と比べ短時間でエッチング廃液から水酸化アルミニウムを分離回収することができる。また、処理時間が短いため、エッチング廃液の処理設備が小規模であっても従来と同等かそれ以上の処理が可能となり、その結果ランニングコストを低く抑えることができる。
また、本発明を実施する上で使用される炭酸ガスは、ボイラーの燃焼排ガス、発酵排ガス、石灰石の焙焼炉等から発生する炭酸ガス、等を用いることができるため、炭酸ガスの調達の必要がなくコストを抑えることができる。
According to the present invention, aluminum hydroxide can be separated and recovered from the etching waste liquid in a shorter time than conventional, as shown in the experimental results in the following examples. In addition, since the processing time is short, even if the processing equipment for the etching waste liquid is small, it is possible to perform processing equivalent to or higher than conventional processing, and as a result, running costs can be kept low.
In addition, carbon dioxide gas used in practicing the present invention may be carbon dioxide gas generated from boiler combustion exhaust gas, fermentation exhaust gas, limestone roasting furnace, etc. There are no costs and costs can be reduced.

さらに、炭酸ガスの吹き込みを2段に分けることによって、1段目では炭酸ソーダを個体で回収し、2段目では炭酸ソーダを溶液で回収することができる。そのため、炭酸ソーダ溶液の回収を所望する場合は、請求項4記載の発明が好適である。   Furthermore, by dividing the blowing of carbon dioxide gas into two stages, sodium carbonate can be recovered individually by the first stage, and sodium carbonate can be recovered by the solution at the second stage. Therefore, when it is desired to recover the sodium carbonate solution, the invention according to claim 4 is suitable.

以上のとおり、本発明によれば、短時間且つ低コストでエッチング廃液から水酸化アルミニウムを分離回収することのできるアルミニウム材の水酸化ナトリウム処理廃液の処理方法を提供することができる。   As described above, according to the present invention, it is possible to provide a method for treating a sodium hydroxide treatment waste liquid of an aluminum material that can separate and recover aluminum hydroxide from an etching waste liquid in a short time and at a low cost.

本発明は既述のごとく、アルミニウムサッシ等の建材の前処理として水酸化ナトリウム溶液によりエッチング処理、続く硫酸溶液中で電解酸化させ、表面に陽極酸化被膜を形成させる廃液のほか、平板印刷版の支持体であるアルミニウム板の粗面化のためのエッチング廃液など、各種の廃液を対象とすることができる。
また、回収した水酸化アルミニウムをポリ塩化アルミニウム又は硫酸バンドの製造に使用することができる。
As described above, the present invention is a pretreatment of a building material such as an aluminum sash, an etching treatment with a sodium hydroxide solution, followed by electrolytic oxidation in a sulfuric acid solution to form an anodized film on the surface, as well as a lithographic printing plate. Various waste liquids such as an etching waste liquid for roughening an aluminum plate as a support can be targeted.
The recovered aluminum hydroxide can be used for the production of polyaluminum chloride or sulfuric acid band.

<実験例>
以下に、本発明に係る実験とその結果とを示す。図1は、本発明に係る実験の実験装置を表している。エッチング廃液を収容可能なガラス製のトールビーカー2は、ウォーターバスの水槽内に満たされた水に漬けられている。このウォーターバス1は、この水槽内に満たされた水を一定の温度が保つことができるようヒーターを備えている。
<Experimental example>
Below, the experiment which concerns on this invention and its result are shown. FIG. 1 shows an experimental apparatus for an experiment according to the present invention. The glass tall beaker 2 that can store the etching waste liquid is immersed in water filled in a water bath tank. The water bath 1 includes a heater so that the water filled in the water tank can be maintained at a constant temperature.

トールビーカー2には、トールビーカー2内に収容されたエッチング廃液の温度を測定可能な温度計9と、トールビーカー2内に収容されたエッチング廃液を図1における下方向端部に取り付けられたプロペラで撹拌可能である攪拌機3と、図1における下方向端部より炭酸ガス及び窒素ガスの混合ガスを噴射可能であるガス吹込管4とが挿入されている。ガス吹込管4に送り込まれる炭酸ガス及び窒素ガスは、それぞれ流量調整弁6、8によって量が調整される。なお、流量の調整はそれぞれのガスの流路に設けられた炭酸ガス流量計7と窒素流量計5とに示される流量を参照しつつ行われる。   The tall beaker 2 includes a thermometer 9 capable of measuring the temperature of the etching waste liquid stored in the tall beaker 2, and a propeller attached to the lower end in FIG. 1 with the etching waste liquid stored in the tall beaker 2. And a gas blowing tube 4 capable of injecting a mixed gas of carbon dioxide and nitrogen gas from the lower end in FIG. 1 are inserted. The amounts of carbon dioxide gas and nitrogen gas fed into the gas blowing pipe 4 are adjusted by the flow rate adjusting valves 6 and 8, respectively. The flow rate is adjusted with reference to the flow rates shown in the carbon dioxide flow meter 7 and the nitrogen flow meter 5 provided in the respective gas flow paths.

本実験に使用したエッチング廃液(以後原液と記す)の組成は下記の通りである。
Na2O :17.3wt%
Al23:12.2wt%
NaOH :12.7wt%
2O他 :57.8wt%
なお、液比重は1.345である。
実験ではトールビーカー2に1リットルの原液を入れ、ウォーターバス1にて反応液温を一定温度に保ち、炭酸ガスを微細化して反応を良くするため、攪拌機3で高速撹拌をしつつ、種々条件を変えて炭酸ガスを供給した。
The composition of the etching waste solution (hereinafter referred to as the stock solution) used in this experiment is as follows.
Na 2 O: 17.3 wt%
Al 2 O 3 : 12.2 wt%
NaOH: 12.7 wt%
H 2 O and others: 57.8 wt%
The liquid specific gravity is 1.345.
In the experiment, 1 liter of undiluted solution was placed in a tall beaker 2, the reaction solution temperature was kept constant in the water bath 1, and the carbon dioxide gas was refined to improve the reaction. The carbon dioxide gas was supplied while changing.

炭酸ガス供給量は、原液の分析値と上記した反応式(2)、(3)より炭酸ソーダに反応する理論値を算出すると259.1グラムであるが、反応率を考慮して10wt%余分に285グラムを供給した。固液分離は濾過ビンを用いて、真空濾過を行った。   The amount of carbon dioxide supplied is 259.1 grams when the theoretical value that reacts with sodium carbonate is calculated from the analytical value of the stock solution and the above reaction formulas (2) and (3), but 10 wt% extra in consideration of the reaction rate Was supplied with 285 grams. Solid-liquid separation was performed by vacuum filtration using a filter bottle.

水酸化アルミニウムの収率は、アルミニウムを基準に算出した。炭酸ガスを規定量供給後直ちに真空濾過を行い、液温が60℃である500ミリリットルの温水にて洗浄して、得られた固形分の水分及び組成分析により算出した。   The yield of aluminum hydroxide was calculated based on aluminum. Immediately after supplying the specified amount of carbon dioxide, vacuum filtration was performed, and the liquid was washed with 500 ml of hot water having a liquid temperature of 60 ° C., and the obtained solid content was calculated by moisture and composition analysis.

炭酸ソーダの収率は、ナトリウムを基準にして算出した。上記濾液と洗浄液を合わせて蒸発乾固により得られた固形分の組成分析により算出した。但し、炭酸ガスの吹き込みを2段に分ける実験では、1段目の反応で得られた固形物の濾過乾燥した固形物の炭酸ソーダ分と、2段目の反応で得られた炭酸ソーダ分の合計量から収率を算出した。   The yield of sodium carbonate was calculated based on sodium. The above filtrate and washing solution were combined and calculated by composition analysis of the solid content obtained by evaporation to dryness. However, in an experiment in which the blowing of carbon dioxide gas is divided into two stages, the solid matter obtained by filtration and drying of the solid matter obtained by the first stage reaction and the sodium carbonate fraction obtained by the second stage reaction are obtained. The yield was calculated from the total amount.

<実験1について>
本実験は、炭酸ガスの供給を2段に分けて行った。本実験では、原液をトールビーカー2に入れ、攪拌機3で撹拌しながら炭酸ガスを供給し、1段目の反応でウォーターバス1にて40℃に保ち、2時間反応させた。この時の炭酸ガス供給量は原液中の水酸化ナトリウムが炭酸ソーダに反応するのに必要な理論量を算出して決めた(103.3グラム)。析出した結晶を濾過分離し、1段目の反応を終えた濾液をトールビーカー2に入れさらに炭酸ガスを供給し、ウォーターバス1にて60℃に保ち2段目の反応を2時間行った。この時の炭酸ガス供給量は原液中のNa2Oが炭酸ソーダに反応するのに必要な理論量を算出して決めた(181.7グラム)。
<About Experiment 1>
In this experiment, carbon dioxide gas was supplied in two stages. In this experiment, the stock solution was put into a tall beaker 2, carbon dioxide gas was supplied while stirring with a stirrer 3, kept at 40 ° C. in the water bath 1 in the first stage reaction, and allowed to react for 2 hours. The amount of carbon dioxide supplied at this time was determined by calculating the theoretical amount necessary for sodium hydroxide in the stock solution to react with sodium carbonate (103.3 grams). The precipitated crystals were separated by filtration, and the filtrate after completion of the first stage reaction was placed in a tall beaker 2 and carbon dioxide gas was further supplied. The water bath 1 was maintained at 60 ° C. and the second stage reaction was carried out for 2 hours. The amount of carbon dioxide supplied at this time was determined by calculating the theoretical amount necessary for Na 2 O in the stock solution to react with sodium carbonate (181.7 grams).

<実験2〜実験5について>
実験2〜実験5は、炭酸ガスの供給を2段に分けず1段で行った。これらの実験では、原液を容器に入れ攪拌機3で撹拌しながら炭酸ガスを供給し、ウォーターバス1にて液温を50℃、60℃、70℃、80℃に保ち、4時間の反応を行った。この時の炭酸ガス供給量は、原液中のNaOHとNa2Oが炭酸ソーダに反応するのに必要な理論量を算出して決めた。
<About Experiment 2 to Experiment 5>
Experiment 2 to Experiment 5 were performed in one stage without supplying carbon dioxide gas in two stages. In these experiments, the stock solution is put in a container and carbon dioxide gas is supplied while stirring with the stirrer 3, and the liquid temperature is kept at 50 ° C., 60 ° C., 70 ° C. and 80 ° C. in the water bath 1 and the reaction is performed for 4 hours. It was. The amount of carbon dioxide supplied at this time was determined by calculating the theoretical amount necessary for NaOH and Na 2 O in the stock solution to react with sodium carbonate.

<実験6について>
本実験は、炭酸ガスの供給を2段に分けず1段で行った。本実験では、原液をトールビーカー2に入れ、攪拌機3で撹拌しながら、炭酸ガスに窒素ガスを加えて炭酸ガス濃度を10%に調節した擬似的なボイラー排ガスを供給し、ウォーターバス1にて液温を60℃に保ち、10時間の反応を行った。この時の炭酸ガス供給量は、原液中のNaOHとNa2Oが炭酸ソーダに反応するのに必要な理論量を算出して決めた。
<About Experiment 6>
In this experiment, the supply of carbon dioxide gas was performed in one stage without being divided into two stages. In this experiment, the stock solution is put into a tall beaker 2 and a pseudo boiler exhaust gas in which carbon dioxide gas concentration is adjusted to 10% by adding nitrogen gas to carbon dioxide while stirring with a stirrer 3 is supplied to the water bath 1. The liquid temperature was kept at 60 ° C. and the reaction was carried out for 10 hours. The amount of carbon dioxide supplied at this time was determined by calculating the theoretical amount necessary for NaOH and Na 2 O in the stock solution to react with sodium carbonate.

Figure 0005160215
Figure 0005160215

以上の結果より、水酸化アルミニウムの収率に着目すると、反応温度が高いほど収率は良くなるが、水分の蒸発によるエッチング廃液の濃縮があり、温度が高いほどガス吹き込み管4、攪拌機3のシャフト、トールビーカー2内壁等に堅い結晶の析出が多くなるため、エッチング廃液の液温を80℃以上に上げるのは望ましくない。また、実験2では50℃で水酸化アルミニウムの収率が62%と低かったが、実装置化する場合、液深を深くしガス分散を良くすることにより反応率は上昇するため、反応温度は50℃〜80℃、好ましくは60から80℃が適している。   From the above results, paying attention to the yield of aluminum hydroxide, the higher the reaction temperature, the better the yield, but there is a concentration of the etching waste liquid due to evaporation of moisture, and the higher the temperature, the more the gas blowing tube 4 and the stirrer 3 Since the precipitation of hard crystals increases on the shaft, the inner wall of the tall beaker 2, etc., it is not desirable to raise the temperature of the etching waste liquid to 80 ° C. or higher. Further, in Experiment 2, the yield of aluminum hydroxide was as low as 62% at 50 ° C., but in the case of actual equipment, the reaction rate increases by increasing the liquid depth and improving gas dispersion. 50 ° C to 80 ° C, preferably 60 to 80 ° C is suitable.

また、実験1における炭酸ソーダの回収については、1段目の炭酸ガスの供給後では固体で回収でき、2段目の炭酸ガスの供給では水酸化アルミニウムの濾液として炭酸ソーダ溶液を回収できるので、固体と溶液と双方が必要な場合、炭酸ガスの供給を2段に分ける方が適している。粉状の需要が多い場合、実験2から実験6に示されるように、炭酸ガスの供給を2段に分けず1段で行い、濾液と洗浄液を合わせて、真空乾燥機、噴霧乾燥機によって容易に粉状で回収できることが本実験で確認できた。   In addition, with regard to the recovery of sodium carbonate in Experiment 1, it can be recovered as a solid after the supply of the first stage carbon dioxide gas, and the sodium carbonate solution can be recovered as the aluminum hydroxide filtrate by the second stage carbon dioxide gas supply. When both a solid and a solution are required, it is better to divide the carbon dioxide supply into two stages. When there is a lot of powdery demand, as shown in Experiment 2 to Experiment 6, the carbon dioxide gas is supplied in one stage without dividing into two stages, and the filtrate and the washing liquid are combined and easily used by a vacuum dryer or a spray dryer. It was confirmed in this experiment that it can be recovered in powder form.

<水酸化アルミニウムおよび炭酸ソーダの利用方法>
次に、本発明に係るエッチング廃液処理のフローと、本発明に係るエッチング廃液の処理過程で生じる水酸化アルミニウムおよび炭酸ソーダの利用方法のフローとの一例を、図2を参照しつつ詳説する。
まず、エッチング廃液の処理フローについて詳説する。エッチング廃液貯留槽21からエッチング廃液を抜き出し、ジャケット内に温水を流し込むことによって槽内を加温可能なエッチング廃液反応槽22に張り込む。エッチング廃液反応槽22内に張り込まれたエッチング廃液の液温を60℃に保ち、攪拌機によって槽内のエッチング廃液を撹拌するとともに炭酸ガスを吹き込む。炭酸ガスを所定量供給した反応液を水酸化アルミニウム濾過器23にかけ、濾液を炭酸ソーダ貯留槽25に移し、水酸化アルミニウム濾過器23内の反応液全量の濾過が終了した後、水酸化アルミニウム濾過器23内の濾滓(ケーキ)を60℃の温水で洗浄することによって水酸化アルミニウムに付着析出した炭酸ソーダを洗い流し、温水で洗浄した水酸化アルミニウムを空気ブローすることによって含水率を15%以下まで下げ、水酸化アルミニウムホッパー24に排出する。洗浄液および空気ブロー液は、5wt%程度の炭酸ソーダを含んでいるため、そのまま廃棄せずに洗浄液貯留槽26に貯留する。炭酸ソーダ貯留槽25に貯留された濾液はスプレードライヤー27において熱風乾燥し、粉体状にして炭酸ソーダホッパー28に貯留し、製品として出荷する。
<Utilization of aluminum hydroxide and sodium carbonate>
Next, an example of the flow of the etching waste liquid treatment according to the present invention and the flow of the utilization method of aluminum hydroxide and sodium carbonate generated during the etching waste liquid treatment process according to the present invention will be described in detail with reference to FIG.
First, the processing flow of the etching waste liquid will be described in detail. The etching waste liquid is extracted from the etching waste liquid storage tank 21, and hot water is poured into the jacket so that the tank is heated to an etching waste liquid reaction tank 22 that can be heated. The temperature of the etching waste liquid stuck in the etching waste liquid reaction tank 22 is maintained at 60 ° C., and the etching waste liquid in the tank is stirred by a stirrer and carbon dioxide gas is blown. The reaction liquid supplied with a predetermined amount of carbon dioxide gas is applied to the aluminum hydroxide filter 23, the filtrate is transferred to the sodium carbonate storage tank 25, and after the filtration of the entire reaction liquid in the aluminum hydroxide filter 23 is finished, the aluminum hydroxide filter Washing the filter cake (cake) in the vessel 23 with hot water at 60 ° C. to wash away sodium carbonate deposited on the aluminum hydroxide, and then blowing the aluminum hydroxide washed with hot water into the water content to 15% or less Until the aluminum hydroxide hopper 24 is discharged. Since the cleaning liquid and the air blowing liquid contain about 5 wt% sodium carbonate, they are stored in the cleaning liquid storage tank 26 without being discarded as they are. The filtrate stored in the sodium carbonate storage tank 25 is dried with hot air in a spray dryer 27, stored in a powdered sodium carbonate hopper 28, and shipped as a product.

次に、エッチング廃液より分離した水酸化アルミニウムからPAC(ポリ塩化アルミニウム)を製造するまでのフローを詳説する。スラリー槽29に濃度が35wt%の塩酸を張り込み、そこに水酸化アルミニウムホッパー24から水酸化アルミニウムを計量して規定量投入し、撹拌することによってスラリー化する。そしてスラリー化した水酸化アルミニウムを、ジャケット内に加熱した蒸気を送り込むことによって槽内を加温可能なPAC反応釜30に移し、常温から100℃まで加熱する。そこからさらに反応釜30内の圧力をゲージ圧0.39メガパスカル、スラリー化した水酸化アルミニウムの温度を150℃として反応釜30を密閉状態として加圧反応させる。そして、反応が終了するとPAC反応釜30のジャケットへの蒸気供給を停止し、PAC反応釜30の内圧を徐々に下げる。次に、PAC反応釜30のジャケットに冷却水を供給し、PAC反応釜30内の反応液の温度を65℃まで下げる。反応液の液温が65℃になったら炭酸ソーダ添加槽31に移し、洗浄液貯留槽26から規定量の炭酸ソーダを抜き出して添加し、攪拌機によって撹拌しつつ1時間反応させた後、第1濾過器32にかけ濾液と濾滓に分離する。第1濾過器32によって分離された濾液は、硫酸ソーダ添加槽33に移し、硫酸ソーダを規定量添加し攪拌機によって撹拌後、第2濾過器34にかけて、PACと濾滓に分離し、PACは製品としてPAC貯留槽35に貯留し、製品として出荷する。   Next, the flow until manufacturing PAC (polyaluminum chloride) from aluminum hydroxide separated from the etching waste liquid will be described in detail. Hydrochloric acid having a concentration of 35 wt% is poured into the slurry tank 29, and a predetermined amount of aluminum hydroxide is metered into the slurry tank 29 from the aluminum hydroxide hopper 24 and stirred to form a slurry. Then, the slurry of aluminum hydroxide is transferred to a PAC reaction kettle 30 that can heat the inside of the tank by feeding steam heated into the jacket, and heated from room temperature to 100 ° C. From there, the pressure in the reaction vessel 30 is further set to a gauge pressure of 0.39 megapascal, the temperature of the slurryed aluminum hydroxide is set to 150 ° C., and the reaction vessel 30 is sealed to cause a pressure reaction. When the reaction is completed, the supply of steam to the jacket of the PAC reaction kettle 30 is stopped, and the internal pressure of the PAC reaction kettle 30 is gradually lowered. Next, cooling water is supplied to the jacket of the PAC reaction kettle 30, and the temperature of the reaction solution in the PAC reaction kettle 30 is lowered to 65 ° C. When the temperature of the reaction liquid reaches 65 ° C., the reaction liquid is transferred to a sodium carbonate addition tank 31, a prescribed amount of sodium carbonate is extracted from the washing liquid storage tank 26 and added, and the reaction is carried out for 1 hour with stirring by a stirrer. It is put into a vessel 32 and separated into filtrate and filter cake. The filtrate separated by the first filter 32 is transferred to a sodium sulfate addition tank 33, a prescribed amount of sodium sulfate is added and stirred by a stirrer, and then passed through a second filter 34 to be separated into PAC and filter cake. Is stored in the PAC storage tank 35 and shipped as a product.

次に、エッチング廃液より分離した水酸化アルミニウムから硫酸バンド(硫酸アルミニウム)を製造するまでのフローを詳説する。反応槽36に、水酸化アルミニウムホッパー24から水酸化アルミニウムを計量して規定量投入し、さらに濃度が98wt%である硫酸を供給する。反応槽36内の反応で得られた反応スラリーは、循環ポンプ37で反応スラリーを循環させることによって撹拌するとともに、空気を吹き込んで空気撹拌することによって反応を促進させ、そのまま1時間反応させる。その後、調整槽38に反応スラリーを移してアルミナ(酸化アルミニウム)の濃度が8wt%となるように水を加える。そして、濃度調整後に第3濾過器39にかけ、そこで得られた濾液を硫酸バンド貯留槽40に貯留し、製品として出荷する。   Next, the flow from manufacturing aluminum sulfate separated from the etching waste liquid to producing a sulfuric acid band (aluminum sulfate) will be described in detail. A predetermined amount of aluminum hydroxide is metered into the reaction tank 36 from the aluminum hydroxide hopper 24, and sulfuric acid having a concentration of 98 wt% is supplied. The reaction slurry obtained by the reaction in the reaction tank 36 is stirred by circulating the reaction slurry with the circulation pump 37, and the reaction is promoted by blowing air and stirring with air, and is allowed to react for 1 hour as it is. Thereafter, the reaction slurry is transferred to the adjustment tank 38 and water is added so that the concentration of alumina (aluminum oxide) is 8 wt%. And after concentration adjustment, it applies to the 3rd filter 39, The filtrate obtained there is stored in the sulfuric acid band storage tank 40, and is shipped as a product.

本発明は、アルミニウム材を水酸化ナトリウム溶液でエッチングすることによって生じるエッチング廃液の処理に適用できるものである。   The present invention is applicable to the treatment of etching waste liquid generated by etching an aluminum material with a sodium hydroxide solution.

本発明に使用した実験装置の概略図である。It is the schematic of the experimental apparatus used for this invention. アルミニウム材の水酸化ナトリウム処理廃液由来産物の製造方法例のフローシートである。It is a flow sheet of the example of the manufacturing method of the sodium hydroxide treatment waste liquid origin product of aluminum material.

1…ウォーターバス、2…トールビーカー、3…攪拌機、4…ガス吹込管、5…窒素流量計、6…流量調整弁、7…炭酸ガス流量計、8…流量調整弁、9…温度計、21…エッチング廃液貯留槽、22…反応槽、23…水酸化アルミニウム濾過器、24…水酸化アルミニウムホッパー、25…炭酸ソーダ貯留槽、26…洗浄液貯留槽、27…スプレードライヤー、28…炭酸ソーダホッパー、29…スラリー槽、30…PAC反応釜、31…炭酸ソーダ添加槽、32…第1濾過器、33…硫酸ソーダ添加槽、34…第2濾過器、35…PAC貯留槽、36…反応槽、37…循環ポンプ、38…調整槽、39…第3濾過器、40…硫酸バンド貯留槽。   DESCRIPTION OF SYMBOLS 1 ... Water bath, 2 ... Tall beaker, 3 ... Stirrer, 4 ... Gas injection pipe, 5 ... Nitrogen flow meter, 6 ... Flow rate adjustment valve, 7 ... Carbon dioxide gas flow meter, 8 ... Flow rate adjustment valve, 9 ... Thermometer, DESCRIPTION OF SYMBOLS 21 ... Etching waste liquid storage tank, 22 ... Reaction tank, 23 ... Aluminum hydroxide filter, 24 ... Aluminum hydroxide hopper, 25 ... Sodium carbonate storage tank, 26 ... Cleaning liquid storage tank, 27 ... Spray dryer, 28 ... Sodium carbonate hopper , 29 ... Slurry tank, 30 ... PAC reaction tank, 31 ... Sodium carbonate addition tank, 32 ... First filter, 33 ... Sodium sulfate addition tank, 34 ... Second filter, 35 ... PAC storage tank, 36 ... Reaction tank 37 ... circulation pump, 38 ... regulating tank, 39 ... third filter, 40 ... sulfuric acid band storage tank.

Claims (5)

アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法によりポリ塩化アルミニウムを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。
(1)前記水酸化ナトリウム処理廃液に、液温が50℃〜80℃の状態で、炭酸ガスを吹き込み、
析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、
(2)前記水酸化アルミニウムの全部または一部を塩酸に加えてスラリー化し、加圧加熱条件下で反応させ、反応スラリーを得る工程、
(3)前記反応スラリーに前記炭酸ソーダの一部を添加して反応させ、濾過により濾液を得る工程、及び
(4)前記濾液に硫酸ソーダを添加して反応させ、濾過により濾液としてポリ塩化アルミニウムを得る工程。
An aluminum characterized in that polyaluminum chloride is produced from a sodium hydroxide treatment waste solution of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of waste aluminum hydroxide treatment liquid.
(1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid in a state where the liquid temperature is 50 ° C. to 80 ° C.,
The precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is in solution or as a solid by drying,
(2) adding all or part of the aluminum hydroxide to hydrochloric acid to form a slurry and reacting under pressure and heating conditions to obtain a reaction slurry;
(3) A step of adding a part of the sodium carbonate to the reaction slurry for reaction, and obtaining a filtrate by filtration; and (4) adding sodium sulfate to the filtrate for reaction, and filtering to form polyaluminum chloride as a filtrate. Obtaining.
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法により硫酸バンドを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。
(1)前記水酸化ナトリウム処理廃液に、液温が50℃〜80℃の状態で、炭酸ガスを吹き込み、
析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、
(2)前記水酸化アルミニウムの全部または一部に硫酸を加え、空気撹拌により反応スラリーを得る工程、
(3)前記反応スラリーに水を加えて濃度を調整した後、濾過により濾液として硫酸バンドを得る工程。
An aluminum material characterized in that a sulfuric acid band is produced from a sodium hydroxide treatment waste liquid of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of aluminum hydroxide waste liquid.
(1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid in a state where the liquid temperature is 50 ° C. to 80 ° C.,
The precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is in solution or as a solid by drying,
(2) adding sulfuric acid to all or a part of the aluminum hydroxide and obtaining a reaction slurry by stirring with air;
(3) A step of adjusting the concentration by adding water to the reaction slurry and then obtaining a sulfate band as a filtrate by filtration.
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法によりポリ塩化アルミニウムを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。An aluminum characterized in that polyaluminum chloride is produced from a sodium hydroxide treatment waste solution of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of waste aluminum hydroxide treatment liquid.
(1)前記水酸化ナトリウム処理廃液に、液温が30℃〜40℃で、炭酸ガスを吹き込むことにより、遊離水酸化ナトリウム分を炭酸ソーダ化して析出させ濾過分離し、  (1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid at a temperature of 30 ° C. to 40 ° C., so that free sodium hydroxide is converted to sodium carbonate, precipitated, separated by filtration,
他方、濾液に、液温が50℃〜80℃で、炭酸ガスを吹き込み、析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、  On the other hand, carbon dioxide is blown into the filtrate at a temperature of 50 ° C. to 80 ° C., and the precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is or as a solid by drying. Process,
(2)前記水酸化アルミニウムの全部または一部を塩酸に加えてスラリー化し、加圧加熱条件下で反応させ、反応スラリーを得る工程、  (2) adding all or part of the aluminum hydroxide to hydrochloric acid to form a slurry and reacting under pressure and heating conditions to obtain a reaction slurry;
(3)前記反応スラリーに前記炭酸ソーダの一部を添加して反応させ、濾過により濾液を得る工程、及び  (3) adding a part of the sodium carbonate to the reaction slurry to cause reaction, and obtaining a filtrate by filtration; and
(4)前記濾液に硫酸ソーダを添加して反応させ、濾過により濾液としてポリ塩化アルミニウムを得る工程。  (4) A step of adding sodium sulfate to the filtrate to cause reaction, and obtaining polyaluminum chloride as a filtrate by filtration.
アルミニウム材を、水酸化ナトリウムを主成分とする溶液で処理することによって生じるアルミニウム材の水酸化ナトリウム処理廃液より、次記の工程を含む方法により硫酸バンドを製造する、ことを特徴とするアルミニウム材の水酸化アルミニウム処理廃液の処理方法。An aluminum material characterized in that a sulfuric acid band is produced from a sodium hydroxide treatment waste liquid of an aluminum material produced by treating the aluminum material with a solution containing sodium hydroxide as a main component by a method including the following steps: Of treatment of aluminum hydroxide waste liquid.
(1)前記水酸化ナトリウム処理廃液に、液温が30℃〜40℃で、炭酸ガスを吹き込むことにより、遊離水酸化ナトリウム分を炭酸ソーダ化して析出させ濾過分離し、  (1) Carbon dioxide gas is blown into the sodium hydroxide treatment waste liquid at a temperature of 30 ° C. to 40 ° C., so that free sodium hydroxide is converted to sodium carbonate, precipitated, separated by filtration,
他方、濾液に、液温が50℃〜80℃で、炭酸ガスを吹き込み、析出する水酸化アルミニウムを濾過分離して回収し、濾液中の炭酸ソーダは、そのまま溶液で又は乾燥によって固体で回収する工程、  On the other hand, carbon dioxide is blown into the filtrate at a temperature of 50 ° C. to 80 ° C., and the precipitated aluminum hydroxide is recovered by filtration, and the sodium carbonate in the filtrate is recovered as it is or as a solid by drying. Process,
(2)前記水酸化アルミニウムの全部または一部に硫酸を加え、空気撹拌により反応スラリーを得る工程、  (2) adding sulfuric acid to all or a part of the aluminum hydroxide and obtaining a reaction slurry by stirring with air;
(3)前記反応スラリーに水を加えて濃度を調整した後、濾過により濾液として硫酸バンドを得る工程。  (3) A step of adjusting the concentration by adding water to the reaction slurry and then obtaining a sulfate band as a filtrate by filtration.
炭酸ガスは、ボイラーの燃焼排ガス、発酵排ガス、石灰石の焙焼炉から発生する炭酸ガスを用いる、請求項1〜4のいずれか1項に記載のアルミニウム材の水酸化ナトリウム処理廃液の処理方法。   The carbon dioxide gas is a treatment method of a sodium hydroxide treatment waste liquid of an aluminum material according to any one of claims 1 to 4, wherein carbon dioxide gas generated from a combustion exhaust gas from a boiler, a fermentation exhaust gas, or a limestone roasting furnace is used.
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