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JPS6053806B2 - Treatment method for sulfuric acid sludge - Google Patents
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JPS6053806B2 - Treatment method for sulfuric acid sludge - Google Patents

Treatment method for sulfuric acid sludge

Info

Publication number
JPS6053806B2
JPS6053806B2 JP6067777A JP6067777A JPS6053806B2 JP S6053806 B2 JPS6053806 B2 JP S6053806B2 JP 6067777 A JP6067777 A JP 6067777A JP 6067777 A JP6067777 A JP 6067777A JP S6053806 B2 JPS6053806 B2 JP S6053806B2
Authority
JP
Japan
Prior art keywords
sulfuric acid
combustion
sludge
gas
acid sludge
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.)
Expired
Application number
JP6067777A
Other languages
Japanese (ja)
Other versions
JPS53144875A (en
Inventor
敦 小林
英敏 原
元紀 大畠
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.)
Kimura Chemical Plants Co Ltd
Original Assignee
Kimura Chemical Plants Co Ltd
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 Kimura Chemical Plants Co Ltd filed Critical Kimura Chemical Plants Co Ltd
Priority to JP6067777A priority Critical patent/JPS6053806B2/en
Publication of JPS53144875A publication Critical patent/JPS53144875A/en
Publication of JPS6053806B2 publication Critical patent/JPS6053806B2/en
Expired legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 本発明は、化学工場等より排出される硫酸スラッジの
処理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating sulfuric acid sludge discharged from chemical factories and the like.

一般に多くの化学工業において、有機物を硫酸で処理
する場合、多量の有機物を含む廃硫酸、所謂硫酸スラッ
ジが排出される。
Generally, in many chemical industries, when organic substances are treated with sulfuric acid, waste sulfuric acid, so-called sulfuric acid sludge, containing a large amount of organic substances is discharged.

例えば、石油工場において、好ましくない種々の炭化
水素留分を除去するために石油留分を濃硫酸で処理する
が、この場合、遊離硫酸と不溶解有機物質及び溶解した
炭化水素類、有機スルフォン酸類等が複雑な組成で含有
された硫酸スラッジが排出される。
For example, in petroleum factories, petroleum fractions are treated with concentrated sulfuric acid to remove various undesirable hydrocarbon fractions, but in this case, free sulfuric acid, undissolved organic substances, dissolved hydrocarbons, and organic sulfonic acids are treated. Sulfuric acid sludge containing a complex composition of

これ等の硫酸スラッジは黒色で刺激臭の強い悪臭を放ち
、放置すれば漸次重合固化し、更に極めて腐食性が大き
いため埋立、海上投棄等は勿論できずその処理には重要
な問題が存す る。 従来より、この種の硫酸スラッジ
の処理方法として種々研究提案されており、その代表的
な方法を以下に述べる。 即ち、硫酸スラッジを燃焼炉
にて噴射燃焼させ硫酸スラッジを熱分解し、含有する硫
黄化合物を二酸化硫黄に分解し、この二酸化硫黄より硫
酸を製造する方法があるが、この方法においては遊離硫
酸を含む硫酸スラッジを直接高温で燃焼さすため、燃焼
炉の損傷も大きく、又、硫酸を製造するための別個の硫
酸製造設備を票要とするため、その処理規模は莫大とな
る。
These sulfuric acid sludges are black in color and emit a strong pungent odor, and if left unattended, they will gradually polymerize and solidify, and are extremely corrosive, so they cannot be buried or dumped at sea, and there are important problems in their disposal. Ru. Conventionally, various research and proposals have been made as methods for treating this type of sulfuric acid sludge, and representative methods will be described below. Specifically, there is a method of injecting and burning sulfuric acid sludge in a combustion furnace to thermally decompose the sulfuric acid sludge, decomposing the sulfur compounds it contains into sulfur dioxide, and producing sulfuric acid from this sulfur dioxide. In this method, free sulfuric acid is Since the sulfuric acid sludge contained therein is directly burned at high temperature, the combustion furnace is seriously damaged, and separate sulfuric acid production equipment is required to produce sulfuric acid, so the scale of the process is enormous.

更に、この燃焼ガスには微量の低分子の有機分解生成物
が含まれるため、製造された硫酸は着色し製品としての
販路が制限される。従つて、その設備投資、補修費、並
びに製品硫酸の品質低下等より考えてごく一部の特殊の
場合を除いて経済的には成立しない。次に、硫酸スラッ
ジに水を加え希釈し、遊離硫酸の濃度を20〜30%に
調節して加熱、加水分解して有機物と硫酸分を分離回収
する方法も提案されているが、この方法によつて回収し
た硫酸は濃度も低く、且つ、加水分解により生成した水
酸基を有する有機物質を相当多量溶解しているので、こ
れを精製するため多大の経費を必要とするのみならず、
分離された有機物質中にも尚相当量の酸成分を含有し、
何等の用途もなく二次公害の原因となるものである。更
に、硫酸スラッジ中の含有する遊離硫酸の濃度を65〜
90%に調整した後、150〜190℃に加熱して、含
有する有機物質を重合、炭化させ炭化物と硫酸を回収す
る方法がある。この方法による場合、生成した炭化物は
イオン吸着能力及び活性炭の能力を有し、且つ、回収硫
酸も比較的良好であるが、この方法においては、硫酸が
有機物質に作用して脱水素反応を行うものであるため、
硫酸が消費される。従つて、硫酸スラッジ中に含有され
る有機物質と硫酸の量の割合に限度があり、遊離硫酸に
対し有機物質が多い場合、別に硫酸を添加する必要があ
ソー般的ではない。このように、従来より提案されてい
る方法は、その処理規模、設備投資、製品の品質並びに
経済性等の問題点から実際に稼動しているものは稀れで
あつて、硫酸スラッジのその殆んどが未処理のまま放置
されているのが現状である。本発明は、低廉な装置と経
費で、その発生現場において硫酸スラッジを完全に無害
に処理する汎用的な方法であつて、即ち、30〜70%
に希釈した水酸化マグネシウムスラリー液に硫酸スラッ
ジを添加、攪拌混合し、PH7以上の泥状のスラッジ中
和物とした後、助燃剤と共に燃焼炉内に供給し温度75
0〜900℃にて燃焼させ、亜硫酸ガスを含む燃焼ガス
をガス吸収塔に導き水酸化マグネシウム懸濁水と気液接
触させ、該亜硫酸ガスを硫酸マグネシウムに変換し水溶
液として放流すると共に、燃焼残渣を中和剤として循環
再使用する硫酸スラッジの処理方法を提供するものであ
る。
Furthermore, since this combustion gas contains trace amounts of low-molecular organic decomposition products, the produced sulfuric acid is colored, which limits its sales as a product. Therefore, considering the equipment investment, repair costs, and quality deterioration of the sulfuric acid product, it is not economically viable except in a few special cases. Next, a method has been proposed in which the sulfuric acid sludge is diluted with water, the concentration of free sulfuric acid is adjusted to 20-30%, and the organic matter and sulfuric acid content are separated and recovered by heating and hydrolysis. Since the sulfuric acid thus recovered has a low concentration and contains a considerable amount of dissolved organic substances having hydroxyl groups produced by hydrolysis, it not only requires a large amount of expense to purify it, but also
The separated organic substances still contain a considerable amount of acid components,
It has no purpose and causes secondary pollution. Furthermore, the concentration of free sulfuric acid contained in the sulfuric acid sludge was increased from 65 to
After adjusting to 90%, there is a method of heating to 150 to 190°C to polymerize and carbonize the organic substances contained, and recover carbide and sulfuric acid. When using this method, the generated carbide has ion adsorption ability and activated carbon ability, and the recovered sulfuric acid is also relatively good. However, in this method, sulfuric acid acts on organic substances to perform a dehydrogenation reaction. Because it is a thing,
Sulfuric acid is consumed. Therefore, there is a limit to the ratio of organic substances and sulfuric acid contained in sulfuric acid sludge, and when the amount of organic substances is large relative to free sulfuric acid, it is not generally necessary to separately add sulfuric acid. As described above, the methods that have been proposed so far are rarely actually put into operation due to problems such as processing scale, equipment investment, product quality, and economic efficiency, and most of them are not used for processing sulfuric acid sludge. The current situation is that most of the waste remains untreated. The present invention is a general-purpose method for completely harmlessly treating sulfuric acid sludge at the site where it is generated, using inexpensive equipment and costs.
Sulfuric acid sludge is added to magnesium hydroxide slurry diluted to 75%, stirred and mixed to form a neutralized muddy sludge with a pH of 7 or higher, and then fed into a combustion furnace together with a combustion improver to a temperature of 75%.
Combustion is carried out at a temperature of 0 to 900°C, and the combustion gas containing sulfur dioxide gas is guided to a gas absorption tower and brought into gas-liquid contact with magnesium hydroxide suspension.The sulfur dioxide gas is converted to magnesium sulfate and discharged as an aqueous solution, and the combustion residue is removed. The present invention provides a method for treating sulfuric acid sludge that is recycled and reused as a neutralizing agent.

以下、図面にもとづいて本発明を説明する。The present invention will be explained below based on the drawings.

図面は、本発明方法の実施例のフローシートであつて、
30〜70%に水で希釈した水酸化マグネシウムスラリ
ー液を導管2を介して中和槽3に供給し、引続き導管1
より硫酸スラッジを中和槽3に供給して攪拌混合し、P
H7以上、好ましくはPH7.〜9の泥状のスラッジ中
和物とする。この際、中和熱により発熱するが通常は特
別に冷却する必要はない。むしろ、好ましくは75℃以
上で充分攪拌混合すればPH7以上で粒子の微細な泥状
のスラッジ中和物となる。次に、中和槽3で生成した泥
状一のスラッジ中和物を導管4を介し燃焼炉5に供給す
る。同時に燃焼炉内で導管6より供給された燈油、重油
等の助燃剤をバーナー等によつて燃焼し、炉内温度を7
50〜900゜Cに保持することによつて該スラッジは
完全に燃焼し、亜硫酸ガスを含む燃焼ガスは導管7を介
し吸収塔8に導入され、同時に酸化マグネシウムを主成
分とする燃焼残渣は導管9を介し残渣貯槽10に排出さ
れ、再び中和剤として循環再使用される。ガス吸収塔8
において、導入された亜硫酸ガスを含む燃焼ガスは導管
11より供給される約1.0〜2.0Wt%の水酸化マ
グネシウム懸濁水と気液接触し、燃焼ガス中の有害な亜
硫酸ガスは吸収酸化され無害マグネシウムに・変換され
水溶液として導管12より排出放流される。一方、亜硫
酸ガスを除去し清浄化された燃焼ガスは無害ガスとして
ガス排出口13より大気中へ放出される。本発明におい
ては、硫酸スラッジをアルカリ剤として30〜70%に
水で希釈した水酸化マグネシウムスラリー液を使用して
中和するが、中和にあたり30%より低い水酸化マグネ
シウムのスラリーを使用すると、スラッジ中和物中の遊
離水分が多量となり必要以上の流動性を生じ、燃焼にあ
たつてそれだけ経済性が低下する。
The drawing is a flow sheet of an embodiment of the method of the present invention,
A magnesium hydroxide slurry solution diluted with water to 30-70% is supplied to the neutralization tank 3 via conduit 2, and then to the neutralization tank 3 through conduit 1.
The sulfuric acid sludge is supplied to the neutralization tank 3, stirred and mixed, and P
H7 or higher, preferably PH7. ~9 slurry-like sludge neutralized product. At this time, heat is generated due to neutralization heat, but there is usually no need for special cooling. Rather, if the mixture is sufficiently stirred and mixed preferably at a temperature of 75° C. or higher, a neutralized sludge with a pH of 7 or higher and fine particles in the form of mud will be obtained. Next, the neutralized sludge produced in the neutralization tank 3 is supplied to the combustion furnace 5 via the conduit 4. At the same time, combustion improvers such as kerosene and heavy oil supplied from the conduit 6 are burned in the combustion furnace using a burner, etc., and the temperature inside the furnace is lowered to 7.
By maintaining the temperature at 50 to 900°C, the sludge is completely combusted, and the combustion gas containing sulfur dioxide gas is introduced into the absorption tower 8 via the conduit 7, and at the same time, the combustion residue containing magnesium oxide as a main component is passed through the conduit. The residue is discharged to a residue storage tank 10 via a filter 9, and is recycled and reused as a neutralizing agent. Gas absorption tower 8
, the introduced combustion gas containing sulfur dioxide gas is brought into gas-liquid contact with approximately 1.0 to 2.0 Wt% magnesium hydroxide suspended water supplied from the conduit 11, and the harmful sulfur dioxide gas in the combustion gas is absorbed and oxidized. It is converted into harmless magnesium and discharged through the conduit 12 as an aqueous solution. On the other hand, the combustion gas that has been purified by removing sulfur dioxide gas is released into the atmosphere from the gas outlet 13 as a harmless gas. In the present invention, sulfuric acid sludge is neutralized using a magnesium hydroxide slurry liquid diluted with water to 30 to 70% as an alkaline agent. However, if a slurry of magnesium hydroxide with a concentration lower than 30% is used for neutralization, The amount of free water in the neutralized sludge increases, resulting in more fluidity than necessary, which reduces the economic efficiency of combustion.

スラリー濃度が70%をこえると、水分量が少なく水酸
化マグネシウムが硫酸と反応すると同時にこのスラッジ
中和物中の水分と結合して硫酸マグネシウムの含水塩と
なり固形化する。固形化した場合、燃焼炉への供給が困
難であるばかりでなく、燃焼炉内の滞留時間を長くして
も固形物の内部まで完全に燃焼するまでには相当の時間
を必要とし、経済的にも不利となり、又、不完全燃焼の
まま燃焼炉より排出すれば、二次処理を要することとな
る。尚、一般工業的に酸性物質を中和する場合、中和剤
として水酸化カルシウム、苛性ソーダ等が用いられるこ
とが多いが、硫酸スラッジの中和にあたつて水酸化カル
シウムを使用すると硫酸との反応生成物の硫酸カルシウ
ムが水に難溶性であるため塊状となり易く、従つて、中
和するためには多量の水を加え流動化させなければなら
ないので燃焼時経済的に不利であり、又、燃焼も不完全
で燃焼残渣は炭化物を含んだ着色した不純な硫酸カルシ
ウムとなり、何等特別の用途もなく二次公害の原因とな
る。又、中和剤として苛性ソータを使用すると水酸化マ
グネシウムより高価であるのみならず、燃焼炉で燃焼す
る際、ナトリウム塩の溶解温度が低いため、燃焼にあた
つて炉壁が溶融し燃焼炉の長期間使用が困難となり、又
、これを防止するため溶融温度以下で燃焼すれば不完全
燃焼となるという欠点がある。しかるに、本発明におい
ては中和剤として水酸化マグネシウムを使用しているの
で、硫酸分は硫酸マグネシウムとなる。しかるに、硫酸
マグネシウムは炭素分の存在で加熱すれば酸化マグネシ
ウムとなるため、このスラッジ中和物を750〜900
℃で燃焼すれば、燃焼残渣中に酸化マグネシウムとして
回収出来、これに水を加えて30〜70%水酸化マグネ
シウムスラリー液に相当するスラリー液とし硫酸スラッ
ジの中和剤として循環再使用出来る利点がある。本発明
においては、水酸化マグネシウムスラリーを中和槽に供
給した後、次に硫酸スラッジを添加して攪拌混合しPH
7以上でスラッジ中和物として(1)るので、中和槽、
配管等並びに燃焼炉等も特に耐食性の優れた高級な材料
を必要としない。
When the slurry concentration exceeds 70%, the water content is low and magnesium hydroxide reacts with sulfuric acid and simultaneously combines with the water in the neutralized sludge to become a hydrated salt of magnesium sulfate and solidify. If solidified, it is not only difficult to feed it to the combustion furnace, but even if the residence time in the combustion furnace is lengthened, it takes a considerable amount of time to completely burn the inside of the solid, making it uneconomical. Moreover, if the fuel is discharged from the combustion furnace with incomplete combustion, secondary treatment will be required. When neutralizing acidic substances in general industry, calcium hydroxide, caustic soda, etc. are often used as neutralizing agents, but if calcium hydroxide is used to neutralize sulfuric acid sludge, it will not react with sulfuric acid. Calcium sulfate, the reaction product, is poorly soluble in water and tends to form lumps. Therefore, in order to neutralize it, a large amount of water must be added to fluidize it, which is economically disadvantageous during combustion. Combustion is incomplete, and the combustion residue becomes colored, impure calcium sulfate containing carbides, which has no special purpose and causes secondary pollution. In addition, when caustic sorter is used as a neutralizing agent, it is not only more expensive than magnesium hydroxide, but also because the melting temperature of sodium salt is low when burned in a combustion furnace, the furnace wall melts during combustion, causing the furnace wall to melt. It is difficult to use it for a long period of time, and if it is burned at a temperature below the melting temperature to prevent this, it has the disadvantage of incomplete combustion. However, in the present invention, since magnesium hydroxide is used as a neutralizing agent, the sulfuric acid component becomes magnesium sulfate. However, since magnesium sulfate becomes magnesium oxide when heated due to the presence of carbon, this sludge neutralized product is
If burned at ℃, it can be recovered as magnesium oxide in the combustion residue, which has the advantage of being able to be recycled and reused as a neutralizing agent for sulfuric acid sludge by adding water to make a slurry liquid equivalent to 30-70% magnesium hydroxide slurry. be. In the present invention, after feeding the magnesium hydroxide slurry to the neutralization tank, sulfuric acid sludge is then added and mixed with stirring to pH
If it is 7 or more, it is treated as a neutralized sludge (1), so a neutralization tank,
Pipes, combustion furnaces, etc. do not require high-grade materials with particularly excellent corrosion resistance.

尚、中和槽は、通常攪拌機付混合槽を使用するが、特に
固形化した硫酸スラッジの場合は中和槽として二ーダー
等の強力な捏和機を用いて流動性が高く粒子の水さい泥
状の中和物とすることが出来る。本発明においては、ス
ラッジ中和物を750〜900℃で燃焼するもので、炉
内温度が750℃より低いと供給されたスラッジ中和物
が完全燃焼せず、又、硫酸マグネシウムが酸化マグネシ
ウムに完全に変換しない。
As the neutralization tank, a mixing tank with an agitator is usually used, but especially in the case of solidified sulfuric acid sludge, a powerful kneading machine such as a kneader is used as a neutralization tank to create a highly fluid and particle-free mixer. It can be made into a slurry-like neutralized product. In the present invention, the sludge neutralized product is burned at a temperature of 750 to 900°C, and if the temperature inside the furnace is lower than 750°C, the supplied sludge neutralized product will not be completely combusted, and the magnesium sulfate will turn into magnesium oxide. Does not convert completely.

又、900℃をこえると助燃剤の消費量が多くなり経済
的に不利となる。一般に亜硫酸ガスの吸収剤として苛性
ソーダ、炭酸ソーダ、或いは水酸化カルシウム、炭酸カ
ルシウム等が使用されるが、ソーダ類は一般に価格が高
く、カルシウム類はスケーリング等の発生が多い。
Moreover, if the temperature exceeds 900°C, the amount of combustion improver consumed increases, which is economically disadvantageous. Generally, caustic soda, soda carbonate, calcium hydroxide, calcium carbonate, etc. are used as absorbents for sulfur dioxide gas, but sodas are generally expensive and calciums often cause scaling.

又、亜硫酸ガスと反応して亜硫酸塩となるためCODが
高くそのまま放流することは出来ない。本発明において
は、吸収剤として水酸化マグネシウムを使用しているの
で、燃焼ガス中に含まれる亜硫酸ガスはソーダ、カルシ
ウム類に比し容易に吸収、酸化され無害な硫酸マグネシ
ウム水容液となるので放流出来るという利点がある。又
、ノズル等の閉塞或いはスケーリング等の発生が殆んど
ないので吸収塔としては、スプレー塔、充填塔、或いは
ベンチユリースクラバーその他いずれの型式のものでも
使用出来る。本発明は上記の如く、稼動中に排出される
硫酸スラッジはもとより、放置され固形化した硫酸スラ
ッジも問題なく簡単な方法で無害な硫酸マグネシウム水
溶液として放流できる硫酸スラッジの完全処理方法であ
る。
In addition, since it reacts with sulfur dioxide gas and becomes sulfite, the COD is high and it cannot be discharged as it is. In the present invention, since magnesium hydroxide is used as an absorbent, the sulfur dioxide gas contained in the combustion gas is more easily absorbed and oxidized than soda or calcium, and becomes a harmless aqueous magnesium sulfate solution. It has the advantage of being able to be released. In addition, since there is almost no occurrence of nozzle clogging or scaling, any type of absorption tower can be used, such as a spray tower, packed tower, or ventilate scrubber. As described above, the present invention is a complete treatment method for sulfuric acid sludge, in which not only sulfuric acid sludge discharged during operation, but also sulfuric acid sludge that has been left to solidify can be discharged as a harmless aqueous magnesium sulfate solution without any problems and in a simple manner.

又、本発明方法によれば装置も特に耐食性の優れた高価
な材料で製作する必要もなく、極めて安価に製作できる
と共に固形化したスラッジ中和物と異なり燃焼炉への供
給も容易で燃焼効果もよく完全に燃焼することが出来、
更に燃焼残渣は硫酸スラッジの中和剤として循環再使用
するもので、何等二次産業廃棄物を放出しない公害防止
上極めて有益な硫酸スラッジの処理方法である。次に本
発明方法の実施例を示す。
In addition, according to the method of the present invention, the equipment does not need to be made of expensive materials with particularly excellent corrosion resistance, and can be manufactured at an extremely low cost. Unlike solidified sludge neutralized material, it is easy to supply to the combustion furnace, and the combustion effect is improved. It can burn well and completely,
Furthermore, the combustion residue is recycled and reused as a neutralizing agent for sulfuric acid sludge, which is an extremely useful method for treating sulfuric acid sludge in terms of pollution prevention without releasing any secondary industrial waste. Next, examples of the method of the present invention will be shown.

実施例1 水酸化マグネシウム(市販品、純度90.14%)40
.7kg、水95k9よりなる水酸化マグネシウムスラ
リー液を中和槽(攪拌機付、容量500e)に供給し、
引きつづき有機物質30%、硫酸62%、水分8%とよ
りなる硫酸スラッジ100kgを加え、攪拌混合した結
果、PH8で有機物質12.7%、硫酸マグネシウム3
2.3%、水分53.5%、その他1.5%の組成より
なる泥状のスラッジ中和物235.7k9を得た。
Example 1 Magnesium hydroxide (commercial product, purity 90.14%) 40
.. A magnesium hydroxide slurry liquid consisting of 7 kg and 95 k9 of water was supplied to a neutralization tank (with a stirrer, capacity 500 e),
Subsequently, 100 kg of sulfuric acid sludge consisting of 30% organic substances, 62% sulfuric acid, and 8% water was added, and as a result of stirring and mixing, the result was a pH of 8 with 12.7% organic substances and 33% magnesium sulfate.
A slurry-like neutralized sludge 235.7k9 was obtained having a composition of 2.3% water, 53.5% water, and 1.5% other.

次に、上記スラッジ中和物を燃焼炉(回転炉床型、12
30m/mφ×700rr!./MH)に供給し燃焼し
た。燃焼条件及び結果は下記の通りである。助熱剤(燈
油)供給量 13.3e/FIRスラッジ中和物
処理量 60.0k9/HR燃焼炉、内部温度
800′C炉出口、燃焼ガス量
320Nd/HR燃焼残渣量
7.5kg/HR上記燃焼ガスを分析した結果、SO2
,CO2,O2,N2等を含有した混合ガスでそのSO
2濃度は12000ppmであつた。
Next, the sludge neutralized product was heated in a combustion furnace (rotary hearth type, 12
30m/mφ×700rr! .. /MH) and burned. The combustion conditions and results are as follows. Heat aid (kerosene) supply amount 13.3e/FIR sludge neutralized product processing amount 60.0k9/HR combustion furnace, internal temperature
800'C furnace outlet, combustion gas amount
320Nd/HR combustion residue amount
7.5kg/HR As a result of analyzing the above combustion gas, SO2
, CO2, O2, N2, etc.
2 concentration was 12000 ppm.

この混合ガスを吸収塔(充填塔、340TrL/WLφ
×5rr1H)に供給し処理した。尚、充填塔には充填
物としてパイレックス#200を高さ2.4Tr1,充
填して使用した。処理条件及び結果は下記の通りである
。ガス空塔速度 1.07n/Sec
吸収液(PH6) 1.5wt.%Mg(0H)2懸
濁水吸収液循環量 4.0f/dガス
入口濃度(SO2) 12000ppmガス
出口濃度(SO2) 10ppm生成硫酸
マグネシウム量 19.0kg/FIR実施例2水
酸化マグネシウム(市販品、純度90.14%)40.
7k9、水17.4k9よりなる水酸化マグネシウムス
ラリー液を実施例1と同じ中和槽に供給し、引きつづき
実施例1と同じ硫酸スラッジ100kgを加え攪拌混合
した結果、PH8で有機物19.0%、硫酸マグネシウ
ム48.1%、水分30.6%、その他2.3%の組成
よりなる泥状のスラッジ中和物158.1kgを得た。
This mixed gas is absorbed into an absorption tower (packed tower, 340TrL/WLφ
×5rr1H) and processed. The packed tower was filled with Pyrex #200 to a height of 2.4Tr1. The processing conditions and results are as follows. Gas superficial velocity 1.07n/Sec
Absorption liquid (PH6) 1.5wt. %Mg(0H)2 suspended water absorption liquid circulating amount 4.0 f/d Gas inlet concentration (SO2) 12000 ppm Gas outlet concentration (SO2) 10 ppm Amount of magnesium sulfate produced 19.0 kg/FIR Example 2 Magnesium hydroxide (commercial product, Purity 90.14%) 40.
A magnesium hydroxide slurry liquid consisting of 7k9 and water 17.4k9 was supplied to the same neutralization tank as in Example 1, and then 100kg of the same sulfuric acid sludge as in Example 1 was added and mixed with stirring. As a result, the organic matter was 19.0% at pH 8. , 158.1 kg of neutralized muddy sludge consisting of 48.1% magnesium sulfate, 30.6% water, and 2.3% others was obtained.

次に、上記スラッジ中和物を実施例1と同じ燃焼炉と吸
収塔を使用して、燃焼及び燃焼ガスを処理した。
Next, the sludge neutralized product was combusted and the combustion gas was treated using the same combustion furnace and absorption tower as in Example 1.

その条件及び結果を下記に示す。燃焼条件及び結果 助熱剤(燈油)供給量 8.0e/HRスラッ
ジ中和物処理量 40.0k9/HR燃焼炉、内
部温度 800℃炉出口、燃焼ガス量
320Nイ/HR燃焼ガス中SO2濃度
13000ppm燃焼残渣量
5.0k9/HR燃焼ガス処理条件及び結果ガス
空塔速度 1.0TrL/Sec吸収
液(PH6) 1.5wt%Mg(0H)2懸濁水吸
収液循環量 4.0e/イガス入口濃
度(SO2) 13000ppmガス出口濃
度(SO2) 20ppm生成硫酸マグ
ネシウム量 19.2k9/8尚、実施例1,2で
得た燃焼残渣を分析した結果その組成は、酸化マグネシ
ウムとして90%、その他硫酸マグネシウム等の無機硫
酸塩を10%含んでいた。
The conditions and results are shown below. Combustion conditions and results Amount of heating aid (kerosene) supplied: 8.0e/HR Amount of neutralized sludge treated: 40.0k9/HR Combustion furnace, internal temperature: 800℃ Furnace outlet, amount of combustion gas: 320N/HR SO2 concentration in combustion gas
13000ppm combustion residue amount
5.0k9/HR Combustion gas processing conditions and results Gas superficial velocity 1.0TrL/Sec Absorption liquid (PH6) 1.5wt% Mg(0H)2 Suspension water absorption liquid circulation amount 4.0e/Igas inlet concentration (SO2) 13000ppm Gas outlet concentration (SO2) 20ppm Amount of magnesium sulfate produced 19.2k9/8 Furthermore, as a result of analyzing the combustion residue obtained in Examples 1 and 2, the composition was 90% as magnesium oxide, and other inorganic sulfuric acid such as magnesium sulfate. Contains 10% salt.

この燃焼残渣に水を加え30〜70%水酸化マグネシウ
ムスラリー液に相当するスラリー液とし硫酸スラッジの
中和剤としてくり返し使用したが別段支障はなかつた。
Water was added to this combustion residue to form a slurry liquid corresponding to a 30-70% magnesium hydroxide slurry liquid, which was repeatedly used as a neutralizer for sulfuric acid sludge without any particular problem.

【図面の簡単な説明】 図面は本発明の実施例のフローシートである。 3・・・・・・中和槽、5・・・・・・燃焼炉、8・・
・・・・ガス吸収塔、10・・・・・・残渣貯槽。
BRIEF DESCRIPTION OF THE DRAWINGS The drawings are flow sheets of embodiments of the present invention. 3... Neutralization tank, 5... Combustion furnace, 8...
...Gas absorption tower, 10...Residue storage tank.

Claims (1)

【特許請求の範囲】[Claims] 1 30〜70%に希釈した水酸化マグネシウムスラリ
ー液に硫酸スラッジを添加、攪拌混合しpH7以上の泥
状のスラッジ中和物とした後、助燃剤と共に燃焼炉内に
供給し温度750〜900℃にて燃焼させ、亜硫酸ガス
を含む燃焼ガスをガス吸収塔に導き水酸化マグネシウム
懸濁水と気液接触させ、該亜硫酸ガスを硫酸マグネシウ
ムに変換し水溶液として放流すると共に、燃焼残渣を中
和剤として循環再使用することを特徴とする硫酸スラッ
ジの処理方法。
1 Add sulfuric acid sludge to magnesium hydroxide slurry diluted to 30 to 70%, stir and mix to obtain a neutralized muddy sludge with a pH of 7 or higher, and then feed it into a combustion furnace together with a combustion improver at a temperature of 750 to 900°C. The combustion gas containing sulfur dioxide gas is led to a gas absorption tower and brought into gas-liquid contact with magnesium hydroxide suspended water, and the sulfur dioxide gas is converted to magnesium sulfate and discharged as an aqueous solution, and the combustion residue is used as a neutralizing agent. A method for treating sulfuric acid sludge characterized by cyclic reuse.
JP6067777A 1977-05-24 1977-05-24 Treatment method for sulfuric acid sludge Expired JPS6053806B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6067777A JPS6053806B2 (en) 1977-05-24 1977-05-24 Treatment method for sulfuric acid sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6067777A JPS6053806B2 (en) 1977-05-24 1977-05-24 Treatment method for sulfuric acid sludge

Publications (2)

Publication Number Publication Date
JPS53144875A JPS53144875A (en) 1978-12-16
JPS6053806B2 true JPS6053806B2 (en) 1985-11-27

Family

ID=13149181

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6067777A Expired JPS6053806B2 (en) 1977-05-24 1977-05-24 Treatment method for sulfuric acid sludge

Country Status (1)

Country Link
JP (1) JPS6053806B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4777025B2 (en) * 2005-09-07 2011-09-21 住友大阪セメント株式会社 Method and apparatus for treating sulfuric acid-containing oily waste
JP2008086866A (en) * 2006-09-29 2008-04-17 Dowa Holdings Co Ltd Solid industrial waste treatment method
CN111023117A (en) * 2019-12-17 2020-04-17 北京科太亚洲生态科技股份有限公司 Closed conveying device and method for rectification residues

Also Published As

Publication number Publication date
JPS53144875A (en) 1978-12-16

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