JPS62278119A - Production of magnesium hydroxide for exhaust gas desulfurization - Google Patents

Production of magnesium hydroxide for exhaust gas desulfurization

Info

Publication number
JPS62278119A
JPS62278119A JP61120853A JP12085386A JPS62278119A JP S62278119 A JPS62278119 A JP S62278119A JP 61120853 A JP61120853 A JP 61120853A JP 12085386 A JP12085386 A JP 12085386A JP S62278119 A JPS62278119 A JP S62278119A
Authority
JP
Japan
Prior art keywords
exhaust gas
magnesium hydroxide
slurry
water
desulfurization
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP61120853A
Other languages
Japanese (ja)
Inventor
Kenichi Nakagawa
健一 中川
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP61120853A priority Critical patent/JPS62278119A/en
Publication of JPS62278119A publication Critical patent/JPS62278119A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F5/00Compounds of magnesium
    • C01F5/14Magnesium hydroxide
    • C01F5/22Magnesium hydroxide from magnesium compounds with alkali hydroxides or alkaline- earth oxides or hydroxides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/46Sulfates
    • C01F11/464Sulfates of Ca from gases containing sulfur oxides

Abstract

PURPOSE:To easily and economically produce Mg(OH)2 suitable for the desulfurization of exhaust gas and utilizable even in the form of aqueous solution, by adding an aqueous solution of a sulfate to an aqueous slurry of Mg(OH)2 containing CaCl2 as a soluble impurity and separating the resultant gypsum dihydride. CONSTITUTION:A reactor 1 is charged with seawater 21 and a Ca compound 22 such as CaO, CaO.MgO, Ca(CH)2, etc. An aqueous slurry of Mg(OH)2 produced by the reaction of the above components is passed through precipitation tanks 2, 3 settle and separate solid impurities such as CaCO3, sand, etc., a flocculant 23 is added and mixed thereto in a mixing tank 4 and the supernatant liquid is taken out of the system and concentrated. The obtained aqueous slurry of Mg(OH)2 containing CaCl2 as a soluble impurity is introduced into a reactor 6. The slurry is mixed with an aqueous solution 11 of a soluble sulfate (e.g. MaSO4) such as desulfurization waste liquid obtained by contacting an aqueous slurry 8 of Mg(OH)2 with an exhaust gas of an exhaust gas generation furnace 9 in an exhaust gas desulfurization apparatus 10. The mixture is vigorously agitated (20) and the produced gypsum dihydride is separated and removed by a wet classifier 7. The obtained aqueous slurry of Mg(OH)2 is stored in a storage tank 8.

Description

【発明の詳細な説明】 3、発明の詳細な説明 [産業上の利用分野] この発明は溶解性不純物として塩化カルシウムが含有さ
れてなる水酸化マグネシウムの水スラリーより上記不純
物に基つくカルシウム基を分離除去して排ガス脱硫用と
して好適な水酸化マグネシウムを得る方法に関する。
Detailed Description of the Invention 3. Detailed Description of the Invention [Industrial Field of Application] This invention is a method for removing calcium groups based on impurities from an aqueous slurry of magnesium hydroxide containing calcium chloride as a soluble impurity. The present invention relates to a method of separating and removing magnesium hydroxide suitable for exhaust gas desulfurization.

〔従来の技術J 近年、排ガス脱硫のための脱硫剤として水酸化マグネシ
ウム[Mg(OH’)]を使用し、排ガス中の二酸化イ
オウ(SO2)を亜硫酸マグネシウムとして固定し、こ
れを空気酸化して水溶性の硫酸マグネシウムとする方法
が相当法まってきている。水酸化マグネシウムは苛性ソ
ーダより安価であり、また水酸化カルシウムなどではス
ケーリングにより運転に支障をきたしやすいのに対し、
このような問題がなく、使用しやすいためである。
[Prior art J] In recent years, magnesium hydroxide [Mg(OH')] has been used as a desulfurizing agent for exhaust gas desulfurization to fix sulfur dioxide (SO2) in the exhaust gas as magnesium sulfite, which is then oxidized in the air. A method using water-soluble magnesium sulfate has become popular. Magnesium hydroxide is cheaper than caustic soda, and calcium hydroxide tends to cause problems with operation due to scaling.
This is because there are no such problems and it is easy to use.

ところで、海水には塩化マグネシウムがかなりの割合で
含まれているため、このマグネシウム基を水酸化マグネ
シウムとして回収利用する試みが古くからなされている
。すなわち、この方法は、海水にCab、CaO−Mg
O,Ca(OH)2などのカルシウム化合物を加えてこ
れと塩化マグネシウムとの反応により水酸化マグネシウ
ムを生成するものである。このように生成される水酸化
マグネシウムは水スラリーの状態にあり、このスラリー
中には炭酸カルシウムなどの不溶性不純物のほか、上記
反応にて副生ずる塩化カルシウムやその他海水中に含ま
れる塩分などの溶解性不純物が多く含まれている。
By the way, since seawater contains a considerable proportion of magnesium chloride, attempts have been made for a long time to recover and use this magnesium group as magnesium hydroxide. That is, this method adds Cab, CaO-Mg to seawater.
Magnesium hydroxide is produced by adding a calcium compound such as O, Ca(OH)2 and reacting it with magnesium chloride. The magnesium hydroxide produced in this way is in the form of a water slurry, and in this slurry, in addition to insoluble impurities such as calcium carbonate, calcium chloride produced as a by-product in the above reaction and other salts contained in seawater are dissolved. Contains many sexual impurities.

マグネシャクリンカ−やゴム充てん剤となる軽焼マグネ
シャなどの製造業者では、これら最終製品が特に高純度
であることが要求されるため、前記方法にて生成される
水酸化マグネシウムの水スラリーから炭酸カルシウムな
どの不溶性不純物を取り除くとともに、大量の水によっ
てスラリー中の溶解性不純物を水洗除去し、このように
精製された高純度の水スラリーをろ過脱水したのち焼成
するなどの方法によって上記目的物を得ている。
Manufacturers of magnesia clinker and lightly calcined magnesia, which is used as a rubber filler, require that their final products be of particularly high purity. In addition to removing insoluble impurities such as calcium, the soluble impurities in the slurry are washed away with a large amount of water, and the thus purified high-purity water slurry is filtered and dehydrated, followed by firing, etc., to obtain the above-mentioned object. It has gained.

一方、排ガス脱硫のための脱硫剤としての水酸化マグネ
シウムは、上記方法にて精製された高純度の水スラリー
の一部を水酸化マグネシウムの濃度が約30重量%とな
る濃度として日本各地の排ガス脱硫工場に船舶やローリ
−車で運搬して使用に供している。
On the other hand, magnesium hydroxide is used as a desulfurizing agent for exhaust gas desulfurization by adding a portion of the high-purity water slurry purified by the above method to a concentration such that the concentration of magnesium hydroxide is approximately 30% by weight. It is transported to the desulfurization plant by ship or lorry for use.

[発明が解決しようとする問題点] しかるに、排ガス脱硫用の脱硫剤に上記の如き高純度の
水スラリーを用いることは経済的に非常に不利である。
[Problems to be Solved by the Invention] However, it is economically very disadvantageous to use the above-mentioned high-purity water slurry as a desulfurization agent for exhaust gas desulfurization.

何故なら、前記大量の水による水洗精製は大規模な設備
を要し、また水洗時の水酸化マグネシウムの沈降分離に
長時間を要し、さらにろ過脱水にも非常に手間がかかる
ため、脱硫剤としての製品コストが高くなってしまうか
らである。
This is because washing and purification using a large amount of water requires large-scale equipment, and it takes a long time to sediment and separate magnesium hydroxide during washing, and furthermore, filtration and dehydration are extremely time-consuming. This is because the product cost becomes high.

したがって、この発明は、排ガス脱硫用の水酸化マグネ
シウムを上記従来の方法に比し経済的有利な方法で得る
“ことを目的としている。
Therefore, it is an object of the present invention to obtain magnesium hydroxide for exhaust gas desulfurization by an economically advantageous method compared to the conventional method described above.

[問題点を解決するための手段] この発明者らは、上記の目的を達成するために鋭意検討
した結果、まず排ガス脱硫用の水酸化マグネシウムとし
てはマグネシャクリンカ−などの原料成分として望まれ
るような高純度品である必要は特になく、炭酸カルシウ
ムを代表とする不溶性不純物と、溶解性不純物のうちの
塩化カルシウムとが可及的に除去されておれば排ガス脱
硫用として支障なく適用できるものであることを知った
[Means for Solving the Problems] As a result of intensive studies to achieve the above object, the inventors found that magnesium hydroxide for exhaust gas desulfurization is desirable as a raw material component for magnesha clinker, etc. It does not need to be a high-purity product; as long as insoluble impurities, such as calcium carbonate, and calcium chloride, which is a soluble impurity, are removed as much as possible, it can be used for exhaust gas desulfurization without any problems. I learned that.

なお、上記の炭酸カルシウムや塩化カルシウムは脱硫装
置内で亜硫酸ガスと反応し、またこの反応後酸化されて
三水せつこう(CaSO4・2H2O)となり、これが
装置内に硬いスケールとなって付着するため、脱流装置
の運転に支障をきたす結果となるものである。
In addition, the above calcium carbonate and calcium chloride react with sulfur dioxide gas in the desulfurization equipment, and after this reaction, they are oxidized to become trihydrate (CaSO4.2H2O), which becomes hard scale and adheres to the inside of the equipment. This results in problems with the operation of the drainage device.

ここで、炭酸カルシウムの如き不溶性不純物は、これが
水酸化マグネシウムに較へて粗大で沈降しやすいもので
あるため、水酸化マグネシウムの水スラリー中から比較
的容易に分離される。一方、塩化カルシウムはこれが水
溶性であるため上記水スラリー中からの除去は容易でな
(、前記従来のダ ような大量夕水を用いた水洗では経済的な問題が生じる
ことになる。
Here, insoluble impurities such as calcium carbonate are coarser and more likely to settle than magnesium hydroxide, and therefore are relatively easily separated from the aqueous slurry of magnesium hydroxide. On the other hand, since calcium chloride is water-soluble, it is not easy to remove it from the water slurry (and washing with a large amount of evening water as in the conventional method causes economical problems).

そこで、この発明者らは、海水にCaOなどのカルシウ
ム化合物を加えて反応させて得た、またこの反射後炭酸
カルシウムなどの不溶性不純物を取り除いた水酸化マグ
ネシウムの水スラリーからこのスラリー中に含まれる塩
化カルシウムをいかにして経済的に分離除去するべきか
につきさらに検討を加えた結果、塩化カルシウム用除去
剤として硫酸マグネシウムの如き水溶性硫酸塩を用いる
ことにより上記目的を達成できるものであることが判っ
た。
Therefore, the present inventors obtained the water slurry of magnesium hydroxide obtained by adding a calcium compound such as CaO to seawater and reacting it, and after this reflection, insoluble impurities such as calcium carbonate were removed. As a result of further studies on how to economically separate and remove calcium chloride, it was found that the above objective could be achieved by using a water-soluble sulfate such as magnesium sulfate as a calcium chloride removal agent. understood.

すなわち、塩化カルシウムが含有されてなる水酸化マグ
ネシウムの水スラリー中に水溶性硫酸塩を含む水溶液を
加えると、たとえば下記の反応式にしたがって三水せつ
こうが生成する。
That is, when an aqueous solution containing a water-soluble sulfate is added to an aqueous slurry of magnesium hydroxide containing calcium chloride, gypsum trihydrate is produced according to the following reaction formula, for example.

CaCl24Mg5O,−MgC12”、 Ca5O,
・2 H2Oこの三水せつこうは粗大粒子であって反応
系外に容易に取り出すことができ、一方副生ずる塩化マ
グネシウムは水スラリー中に混入してくるがこれを排ガ
ス脱硫装置内に導いてもスケーリングの問題がなく、し
たがって二本せつこうが除去された水スラリーは排ガス
脱硫用の脱硫剤としてそのまま使用に供することができ
る。このため、従来のような大量の水を用いた水洗工程
が不要となり、経済的かつ容易に排ガス脱硫用の水酸化
マグネシウムの水スラリーが得られることになる。
CaCl24Mg5O, -MgC12'', Ca5O,
・2H2O This trihydrate is a coarse particle and can be easily taken out of the reaction system, while by-product magnesium chloride is mixed into the water slurry, but even if it is introduced into the exhaust gas desulfurization equipment. There is no problem of scaling, and therefore the water slurry from which the two plasters have been removed can be used as is as a desulfurization agent for exhaust gas desulfurization. Therefore, the water washing process using a large amount of water as in the conventional method is not necessary, and a water slurry of magnesium hydroxide for exhaust gas desulfurization can be obtained economically and easily.

この発明は、上記の知見に基ついてなされたものであり
、その要旨とするところは、溶解性不純物として塩化カ
ルシウムが含有されてなる水酸化マグネシウムの水スラ
リーに水溶性硫酸塩を含む水溶液を加えて反応させたの
ち、反応生成物としての二本せつこうを上記水スラリー
中から分離除去することを特徴とする排ガス脱硫用水酸
化マグネシウムの製造方法にある。
This invention was made based on the above findings, and its gist is that an aqueous solution containing a water-soluble sulfate is added to an aqueous slurry of magnesium hydroxide containing calcium chloride as a soluble impurity. The present invention provides a method for producing magnesium hydroxide for exhaust gas desulfurization, characterized in that after the reaction, two gypsum as a reaction product is separated and removed from the water slurry.

[発明の構成・作用] 以下、この発明方法を図面を参考にして詳しく説明する
[Structure and operation of the invention] Hereinafter, the method of the invention will be explained in detail with reference to the drawings.

図中、1は水酸化マグネシウムの水スラリーを生成させ
るための反応槽、2,3は上記水スラリー中の不溶性固
形不純物を分離除去するための沈降槽、4は上記固形不
純物が分離除去された水スラリーに水酸化マグネシウム
を凝集沈降させやすくするための凝集剤を加える混合槽
、5は上記凝集剤が加えられた水スラリーを静置して水
酸化マグネシウムを沈降させるための濃縮槽、6は上記
濃縮された水酸化マグネシウムの水スラリーに硫酸マグ
ネシウムを含む水溶液を加えて水スラリー中の塩化カル
シウムと硫酸マグネシウムとを反応させるための反応槽
、7は湿式サイクロンの如き湿式分級機、8は上記分級
機7によって塩化カルシウムと硫酸マグネシウムとの反
応物である二本せつこうを分離除去したのちの排ガス脱
硫用の水酸化マグネシウムの水スラリーの貯留槽である
In the figure, 1 is a reaction tank for producing a water slurry of magnesium hydroxide, 2 and 3 are settling tanks for separating and removing insoluble solid impurities in the water slurry, and 4 is a tank for separating and removing the solid impurities. 5 is a mixing tank in which a flocculant is added to the water slurry to facilitate coagulation and sedimentation of magnesium hydroxide; 5 is a concentration tank in which the water slurry to which the flocculant has been added is allowed to stand; 6 is a concentration tank in which the magnesium hydroxide is precipitated; A reaction tank for adding an aqueous solution containing magnesium sulfate to the concentrated magnesium hydroxide water slurry to cause the calcium chloride and magnesium sulfate in the water slurry to react; 7 is a wet classifier such as a wet cyclone; 8 is the above-mentioned This is a storage tank for aqueous slurry of magnesium hydroxide for exhaust gas desulfurization after the classifier 7 separates and removes a reaction product of calcium chloride and magnesium sulfate.

9は重油たき燃焼炉やボイラーなどの排ガス発生炉、1
0は排ガス脱硫装置、11は上記装置10内で生成した
硫酸マグネシウムを含む水溶液、つまり脱硫排液の貯留
槽、12,13,14,15.16.17はポンプ、1
8,19.2Oはそれぞれ撹拌羽根18a。
9 is an exhaust gas generating furnace such as a heavy oil-fired combustion furnace or boiler, 1
0 is an exhaust gas desulfurization device; 11 is a storage tank for an aqueous solution containing magnesium sulfate generated in the device 10, that is, a desulfurization waste liquid; 12, 13, 14, 15, 16, and 17 are pumps;
8 and 19.2O are stirring blades 18a, respectively.

19a、2Oaが付設された撹拌機、21は海水タンク
、22はCa0%CaO−Mg0%Ca(OH)などの
カルシウム化合物の水スラリータンク、23は凝集剤タ
ンクである。
19a, a stirrer equipped with 2Oa, 21 a seawater tank, 22 a water slurry tank for a calcium compound such as Ca0%CaO-Mg0%Ca(OH), and 23 a flocculant tank.

上記構成の装置において、まず反応槽1内で海水タンク
21より供給された海水にカルシウム化合物の水スラリ
ータンク22より上記化合物を加えて撹拌機18によっ
て強力撹拌することにより海水中の塩化マグネシウムと
上記化合物との反応を行わせて水酸化マグネシウムの水
スラリーを生成する。この反応により水溶性不純物であ
る塩化カルシウムが副生じ水スラリー中に混入してくる
In the apparatus configured as described above, first, the above compound is added from the calcium compound water slurry tank 22 to the seawater supplied from the seawater tank 21 in the reaction tank 1, and the above compound is strongly stirred by the stirrer 18, whereby the magnesium chloride in the seawater and the above described compound are added. The reaction with the compound produces a slurry of magnesium hydroxide in water. As a result of this reaction, calcium chloride, which is a water-soluble impurity, is mixed into the water slurry as a by-product.

また、上記反応のほか海水中の重炭酸カルシウム[Ca
 (HCO3)2 ]と水水酸化カルシラとの反応がお
こって固形不純物としての炭酸カルシウムか生成し、水
スラリー中に混入してくる。
In addition to the above reaction, calcium bicarbonate [Ca
(HCO3)2 ] and Calcilla hydroxide to produce calcium carbonate as a solid impurity, which is mixed into the water slurry.

このような不純物を含む上記水スラリーは沈降槽2,3
に導かれて炭酸カルシウムや海水中に含まれる砂などの
固形不純物が沈降分離され、ポンプ13により糸外へ取
り出される。このようにして固形不純物が分離除去され
た水スラリーはついで混合槽4に導かれ、凝集剤タンク
23によって供給されるアルミ系などの凝集剤を水スラ
リー巾約1 ppmの濃度で撹拌機19によって強力に
撹拌混合する。
The water slurry containing such impurities is sent to settling tanks 2 and 3.
solid impurities such as calcium carbonate and sand contained in the seawater are sedimented and separated, and are taken out of the yarn by the pump 13. The water slurry from which the solid impurities have been separated and removed in this way is then led to the mixing tank 4, where a flocculant such as aluminum, supplied from the flocculant tank 23, is added to the water slurry at a concentration of about 1 ppm by the agitator 19. Stir vigorously to mix.

この混合物を濃縮槽5に導いて静置することにより、水
スラリー中の水酸化マグネシウムが沈降し、上澄液は系
外に取り出される。取り出された上澄液は排海水として
PHを7〜8程度に調整して海に戻す。一方、沈降によ
って濃縮された水酸化マグネシウムの水スラリーはポン
プ14によって反応槽6に導入される。このときのスラ
リーの水酸化マグネシウムの濃度としては7〜10重量
%程度である。
By introducing this mixture into the concentration tank 5 and allowing it to stand still, the magnesium hydroxide in the water slurry is precipitated, and the supernatant liquid is taken out of the system. The removed supernatant liquid is returned to the sea as drained seawater with a pH adjusted to about 7 to 8. On the other hand, a water slurry of magnesium hydroxide concentrated by sedimentation is introduced into the reaction tank 6 by a pump 14. The concentration of magnesium hydroxide in the slurry at this time is about 7 to 10% by weight.

反応槽6では貯留槽11より硫酸マグネシウムを3〜1
0重量%程度含む水溶液が供給され撹拌機2Oによって
強力撹拌されることにより、前記水スラリー中に含まれ
る溶解性不純物としての塩化カルシウムと硫酸マグネシ
ウムとが反応し、ニ水せつこうが生成する。この二本せ
つこうは粒子が粗大で沈降分離しやすいものであるため
、ポンプ15によって反応液を湿式分級機へ供給するこ
とにより容易に分離され、分離された二本せつこうは前
記沈降槽3に導かれてこれに混入してくる少量の水酸化
マグネシウムの水スラリーを回収するとともに、ポンプ
13により前記した炭酸カルシウムなどの固形不純物と
一緒に系外へ取り出される。
In the reaction tank 6, 3 to 1 parts of magnesium sulfate is added from the storage tank 11.
When an aqueous solution containing about 0% by weight is supplied and strongly stirred by the stirrer 2O, calcium chloride as a soluble impurity contained in the water slurry reacts with magnesium sulfate, and dihydric gypsum is produced. Since these two plasters have coarse particles and are easily separated by sedimentation, they are easily separated by supplying the reaction liquid to the wet classifier using the pump 15, and the separated two plasters are separated from the sedimentation tank 3. A small amount of the water slurry of magnesium hydroxide that is introduced into the slurry and mixed therein is recovered and taken out of the system together with the solid impurities such as calcium carbonate mentioned above by the pump 13.

このようにして二本せつこうが分離除去された水酸化マ
グネシウムの水スラリーは、排ガス脱硫用の脱硫剤とし
て支障なく利用できるものであり、排ガス脱硫装置10
に供給するための脱硫剤として貯留槽8に貯留される。
The water slurry of magnesium hydroxide from which the two plasters have been separated and removed in this way can be used without any problem as a desulfurization agent for exhaust gas desulfurization, and can be used in the exhaust gas desulfurization equipment 10.
The desulfurizing agent is stored in a storage tank 8 as a desulfurizing agent to be supplied to the water.

排ガス脱硫装置10においては、排ガス発生炉9の排ガ
スが導入されこれに貯留槽8の水スラリーを供給するこ
とにより、排ガス中の亜硫酸ガスと水酸化マグネシウム
とが反応し、またこの反応後酸化されることにより硫酸
マグネシウムが生成する。この硫酸マグネシウムを含む
水溶液、つまり脱硫排液は硫酸マグネシウムが前記濃度
となった時点でポンプ17により装置外へ取り出され貯
留槽11に貯留され、その一部は排液として海に投棄さ
れ、残りは前記反応槽6へ供給するための反応試剤とし
て利用される。
In the exhaust gas desulfurization device 10, the exhaust gas from the exhaust gas generation furnace 9 is introduced and the water slurry from the storage tank 8 is supplied to it, so that the sulfur dioxide gas in the exhaust gas and magnesium hydroxide react, and after this reaction, oxidized This produces magnesium sulfate. This aqueous solution containing magnesium sulfate, that is, the desulfurization waste liquid, is taken out of the device by the pump 17 when the magnesium sulfate reaches the above concentration and is stored in the storage tank 11. A part of it is dumped into the sea as waste liquid, and the rest is used as a reaction reagent to be supplied to the reaction tank 6.

なお、上記の例では水溶性硫酸塩として硫酸マグネシウ
ムを用いているが、その他硫酸すl−IJウムなどの水
溶性の硫酸塩であれば上記と同様に使用できる。また、
上記例では、溶解性不純物として塩化カルシウムが含有
されてなる水酸化マグネシウムの水スラリーとして、海
水にCaO,CaO・MgO、Ca (OH)2などの
カルシウム化合物を加えて反応させて得られたものを用
いているが、上記水スラリーはこれ以外の方法で得られ
たものであってもよい。
Although magnesium sulfate is used as the water-soluble sulfate in the above example, any other water-soluble sulfate such as sodium sulfate can be used in the same manner as above. Also,
In the above example, an aqueous slurry of magnesium hydroxide containing calcium chloride as a soluble impurity is obtained by adding and reacting calcium compounds such as CaO, CaO・MgO, and Ca(OH)2 to seawater. However, the water slurry may be obtained by other methods.

すなわち、この発明は上記水スラリー中に含まれる塩化
カルシウムを分離除去する手段に特徴を有するものであ
るから、上記水スラリーは上述の海水から生成したもの
に限らず、他の方法で生成されたものであってもよいの
である。たとえば石炭燃焼排ガスを水酸化マグネシウム
の水スラリーで脱硫した脱硫排液中には硫酸マグネシウ
ムとともにかなりの割合の塩化マグネシウムが含まれて
おり、この排液を水酸化カルシウムで処理すると二本せ
つこうと水酸化マグネシウムが生成し、二本せつこうを
分離除去することにより水酸化マグネシウムの水スラリ
ーが得られる。ところが、この水スラリー中には塩化マ
グネシウムと水酸化カルシウムとの反応によって生じる
塩化カルシウムか混入してくるため、これをそのまま排
ガス脱硫用の脱硫剤としては使用できず、この発明の方
法を適用して上記塩化カルシウムを除去することにより
脱硫剤としての利用が可能となる。
That is, since this invention is characterized by a means for separating and removing calcium chloride contained in the water slurry, the water slurry is not limited to the one produced from seawater as described above, but can also be produced by other methods. It can also be something. For example, the desulfurization waste obtained by desulfurizing coal combustion exhaust gas with a water slurry of magnesium hydroxide contains a considerable proportion of magnesium chloride as well as magnesium sulfate. Magnesium oxide is produced, and by separating and removing the two plasters, an aqueous slurry of magnesium hydroxide is obtained. However, since calcium chloride produced by the reaction between magnesium chloride and calcium hydroxide is mixed into this water slurry, it cannot be used as it is as a desulfurizing agent for exhaust gas desulfurization, so the method of this invention is not applied. By removing the above-mentioned calcium chloride, it becomes possible to use it as a desulfurization agent.

〔発明の効果」 以上のように、この発明においては、溶解性不純物とし
て塩化カルシウムが含有されてなる水酸化マグネシウム
の水スラリーより上記不純物に基つくカルシウム基を分
離除去するための除去剤として水溶性硫酸塩を含む水溶
液を用いたことにより、排ガス脱硫用の脱硫剤として支
障なく応用できる水酸化マグネシウムを経済的かつ容易
に製造できるという効果が得られる。また、上記水溶性
硫酸塩として特に硫酸マグネシウムを用いたときには、
この硫酸マグネシウムを含む水溶液として排ガス脱硫装
置で得られる脱硫排液をそのまま利用できるから、この
点からも経済性の向上が期待される。
[Effects of the Invention] As described above, in this invention, a water-soluble removal agent is used as a removing agent for separating and removing calcium groups based on impurities from an aqueous slurry of magnesium hydroxide containing calcium chloride as a soluble impurity. By using an aqueous solution containing a chemical sulfate, it is possible to economically and easily produce magnesium hydroxide, which can be used without any problems as a desulfurizing agent for exhaust gas desulfurization. In addition, when magnesium sulfate is used as the water-soluble sulfate,
Since the desulfurization waste liquid obtained from the exhaust gas desulfurization apparatus can be used as it is as an aqueous solution containing magnesium sulfate, improvement in economic efficiency is also expected from this point of view.

さらに、排ガス脱硫装置が海岸付近に設置されている場
合には、海水にCaOなどのカルシウム化合物を反応さ
せることによって溶解性不純物として塩化カルシウムを
含む水酸化マグネシウムの水スラリーが得られ、この水
スラリーに上記装置から排出される脱硫排液を反応させ
ることで上記装置内に供給可能な脱硫剤が得られるから
、つまりこの発明の方法を排ガス脱硫工場において上述
のとおり実用化することにより、前記従来のようにマグ
ネシャクリンカ−などの製造業者が製造した中間原料と
しての水酸化マグネシウムの水スラリーを日本各地の排
ガス脱硫工場に運搬するといった手間が省けて運搬費な
どのコストが不要となるため、経済性のより一層の改善
を図れることになる。
Furthermore, when the exhaust gas desulfurization equipment is installed near the coast, a water slurry of magnesium hydroxide containing calcium chloride as a soluble impurity is obtained by reacting seawater with calcium compounds such as CaO, and this water slurry By reacting the desulfurization waste liquid discharged from the above apparatus, a desulfurizing agent that can be supplied into the above apparatus can be obtained.In other words, by putting the method of the present invention into practical use in an exhaust gas desulfurization factory as described above, This eliminates the hassle of transporting the magnesium hydroxide water slurry as an intermediate raw material produced by manufacturers of magnesha clinkers and other products to exhaust gas desulfurization plants across Japan, and eliminates costs such as transportation costs. This will further improve economic efficiency.

〔実施例1 以下に、この発明の実施例を記載してより具体的に説明
する。
[Example 1] Examples of the present invention will be described below to explain more specifically.

実施例 図面に示す装置を用いて、反応槽1に18トン/時間の
速度で海水を導き、ここにCaOの7重量%の水スラリ
ーをPHが10,4〜10.6の範囲となるように供給
した。反応液を沈降槽2,3に供給して沈降槽3の下部
より固形不純物としての炭酸カルシウム、砂等を分離除
去した。沈降槽2よりオーバフローする水酸化マグネシ
ウムの水スラリーに混合槽4においてアルミ系の凝集剤
(第一工業製薬社製の商品名PAC)を水スラリー中l
ppmの濃度となるように添加したのち、濃縮槽5で静
置して水酸化マグネシウムを沈降させた。
Example Using the apparatus shown in the drawings, seawater was introduced into the reaction tank 1 at a rate of 18 tons/hour, and a water slurry containing 7% by weight of CaO was added thereto so that the pH would be in the range of 10.4 to 10.6. supplied. The reaction solution was supplied to settling tanks 2 and 3, and solid impurities such as calcium carbonate and sand were separated and removed from the lower part of settling tank 3. In the mixing tank 4, an aluminum-based coagulant (trade name: PAC manufactured by Dai-ichi Kogyo Seiyaku Co., Ltd.) is added to the water slurry of magnesium hydroxide overflowing from the settling tank 2.
After adding the solution to a concentration of ppm, it was allowed to stand in the concentration tank 5 to precipitate magnesium hydroxide.

沈降した水酸化マグネシウムを含む水スラIJ−を50
0Kg/時間の速度で反応槽6に導いた。なお、上記水
スラリー中の水酸化マグネシウムの濃度は7重量%であ
った。この反応槽6に貯留槽11より硫酸マグネシウム
が3重量%の濃度で含まれた水溶液(脱硫排液)を40
h/時間の速度で供給し、反応させた。反応液中には水
酸化マグネシウムと三水せつこうが重量比97:3の割
合で含まれており、これを湿式分級機(湿式サイクロン
)7に導き、三水せつこうを分離した。三水せつこうが
分離された水酸化マグネシウムの水スラリーは上記分級
機7よりオーバーフローさせて貯留槽8に貯留した。
50 ml of water slug IJ- containing precipitated magnesium hydroxide
It was introduced into the reaction tank 6 at a rate of 0 kg/hour. Note that the concentration of magnesium hydroxide in the water slurry was 7% by weight. 40% of an aqueous solution (desulfurization waste liquid) containing magnesium sulfate at a concentration of 3% by weight was added to the reaction tank 6 from the storage tank 11.
It was fed and reacted at a rate of h/h. The reaction solution contained magnesium hydroxide and gypsum trihydrate at a weight ratio of 97:3, and was led to a wet classifier (wet cyclone) 7 to separate the gypsum trihydrate. The water slurry of magnesium hydroxide from which the gypsum was separated was allowed to overflow from the classifier 7 and stored in a storage tank 8.

この水酸化マグネシウムの水スラリーを、排ガス発生炉
9からの排ガス(硫黄酸化物・1,500ppm、酸素
含有量4%)を9,00ONm/時間の量で導入させて
なる脱硫装置内に、500Kg/時間の速度で供給し脱
硫反応を行わせた。脱硫排液は3重量%の硫酸マグネシ
ウムを含む水溶液として貯留槽11に導き、ここでPH
を調整した上でその一部を反応槽6に連続供給するよう
にした。
500 kg of this water slurry of magnesium hydroxide was introduced into a desulfurization equipment in which exhaust gas (sulfur oxides: 1,500 ppm, oxygen content: 4%) from the exhaust gas generating furnace 9 was introduced at a rate of 9,00 Nm/hour. /hour to carry out the desulfurization reaction. The desulfurization waste liquid is led to the storage tank 11 as an aqueous solution containing 3% by weight of magnesium sulfate, where the PH
After adjusting the amount, a part of the amount was continuously supplied to the reaction tank 6.

このようにして連続運転を行うことにより、脱硫装置1
0内でスケーリングなどの問題をきたすことなく長期に
わたって安定した脱硫処理を行えた。
By performing continuous operation in this way, the desulfurization equipment 1
Desulfurization treatment could be carried out stably over a long period of time without causing problems such as scaling within the range of 0.

【図面の簡単な説明】[Brief explanation of the drawing]

図面はこの発明の方法を適用した装置構成例を示す概略
図である。 5・・水酸化マグネシウムの水スラリー用濃縮槽、6・
・反応槽、7・・・三水せつこう分1離用の湿式分級機
、8・・脱硫用水酸化マグネシウムの水スラリーの貯留
槽、11・・・硫酸マグネシウムを含む水溶液の貯留槽 特許出願人  中  川  健  − 1)Jalコ
The drawing is a schematic diagram showing an example of a device configuration to which the method of the present invention is applied. 5. Concentrating tank for magnesium hydroxide water slurry, 6.
・Reaction tank, 7... Wet classifier for separation of gypsum trihydrate, 8... Storage tank for water slurry of magnesium hydroxide for desulfurization, 11... Storage tank for aqueous solution containing magnesium sulfate Patent applicant Ken Nakagawa - 1) Jalco

Claims (4)

【特許請求の範囲】[Claims] (1)溶解性不純物として塩化カルシウムが含有されて
なる水酸化マグネシウムの水スラリーに水溶性硫酸塩を
含む水溶液を加えて反応させたのち、反応生成物として
の二水せつこう(CaSO_4・2H_2O)を上記水
スラリー中から分離除去することを特徴とする排ガス脱
硫用水酸化マグネシウムの製造方法。
(1) After adding an aqueous solution containing a water-soluble sulfate to an aqueous slurry of magnesium hydroxide containing calcium chloride as a soluble impurity and causing a reaction, gypsum dihydrate (CaSO_4.2H_2O) is produced as a reaction product. A method for producing magnesium hydroxide for exhaust gas desulfurization, which comprises separating and removing from the water slurry.
(2)溶解性不純物として塩化カルシウムが含有されて
なる水酸化マグネシウムの水スラリーが海水にCaO、
CaO・MgO、Ca(OH)_2などのカルシウム化
合物を加えて反応させて得られる水スラリーからなる特
許請求の範囲第(1)項記載の排ガス脱硫用水酸化マグ
ネシウムの製造方法。
(2) Water slurry of magnesium hydroxide containing calcium chloride as a soluble impurity is added to seawater with CaO,
A method for producing magnesium hydroxide for exhaust gas desulfurization according to claim (1), which comprises a water slurry obtained by adding and reacting calcium compounds such as CaO.MgO and Ca(OH)_2.
(3)水溶性硫酸塩が硫酸マグネシウムである特許請求
の範囲第田項または第(2)項記載の排ガス脱硫用水酸
化マグネシウムの製造方法。
(3) The method for producing magnesium hydroxide for exhaust gas desulfurization according to claim 1 or (2), wherein the water-soluble sulfate is magnesium sulfate.
(4)硫酸マグネシウムを含む水溶液が排ガスに水酸化
マグネシウムの水スラリーを接触させて得られる脱硫排
液からなる特許請求の範囲第(3)項記載の排ガス脱硫
用水酸化マグネシウムの製造方法。
(4) The method for producing magnesium hydroxide for exhaust gas desulfurization according to claim (3), wherein the aqueous solution containing magnesium sulfate is a desulfurization waste obtained by contacting exhaust gas with an aqueous slurry of magnesium hydroxide.
JP61120853A 1986-05-26 1986-05-26 Production of magnesium hydroxide for exhaust gas desulfurization Pending JPS62278119A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61120853A JPS62278119A (en) 1986-05-26 1986-05-26 Production of magnesium hydroxide for exhaust gas desulfurization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61120853A JPS62278119A (en) 1986-05-26 1986-05-26 Production of magnesium hydroxide for exhaust gas desulfurization

Publications (1)

Publication Number Publication Date
JPS62278119A true JPS62278119A (en) 1987-12-03

Family

ID=14796564

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61120853A Pending JPS62278119A (en) 1986-05-26 1986-05-26 Production of magnesium hydroxide for exhaust gas desulfurization

Country Status (1)

Country Link
JP (1) JPS62278119A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101346348B1 (en) * 2011-07-13 2014-01-02 일솜 주식회사 Apparatus for preparing magnesium hydroxide from bitterns

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101346348B1 (en) * 2011-07-13 2014-01-02 일솜 주식회사 Apparatus for preparing magnesium hydroxide from bitterns

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