JPH10249148A - Exhaust gas treating agent and production thereof - Google Patents

Exhaust gas treating agent and production thereof

Info

Publication number
JPH10249148A
JPH10249148A JP9275721A JP27572197A JPH10249148A JP H10249148 A JPH10249148 A JP H10249148A JP 9275721 A JP9275721 A JP 9275721A JP 27572197 A JP27572197 A JP 27572197A JP H10249148 A JPH10249148 A JP H10249148A
Authority
JP
Japan
Prior art keywords
exhaust gas
calcium hydroxide
added
water
treating agent
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.)
Granted
Application number
JP9275721A
Other languages
Japanese (ja)
Other versions
JP3273907B2 (en
Inventor
Yujiro Iwamoto
勇二郎 岩本
Keiji Kokubo
啓二 小久保
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.)
RYOKO SEKKAI KOGYO KK
Original Assignee
RYOKO SEKKAI KOGYO KK
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 RYOKO SEKKAI KOGYO KK filed Critical RYOKO SEKKAI KOGYO KK
Priority to JP27572197A priority Critical patent/JP3273907B2/en
Publication of JPH10249148A publication Critical patent/JPH10249148A/en
Application granted granted Critical
Publication of JP3273907B2 publication Critical patent/JP3273907B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an exhaust gas treating agent that removes harmful oxides in exhaust gas with high efficiency, prevent sticking and clogging to a piping, has good powder flow property at a time of being produced, has low viscosity in a slurry state at the time of treating the exhaust gas, does not generate offensive smell at a keeping and storage time, unnecessitates severe control against fire, enables easy disposal of the agent because of the high strength at a time of being solidified with cement after a treatment of the exhaust gas, and lessens the pressure drop of a bag filter after a treatment of the exhaust gas. SOLUTION: This exhaust gas treating agent consists essentially of calcium hydroxide and incorporates 0.1-10wt.% hexitol against the calcium hydroxide and has >=40m<2> /g specific surface areas, and 7-15μm average sizes. When the calcium hydroxide is mixed with water, hexitol is mixed at a ratio of 0.1-10wt.% for the calcium oxide to digest the calcium oxide, thus the exhaust gas treating agent is produced.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は水酸化カルシウムを
主要成分とする排ガス処理剤及びその製造方法に関す
る。更に詳しくは都市ゴミの焼却炉、火力発電所、電気
炉等から排出される燃焼排ガスの浄化に適する排ガス処
理剤及びその製造方法に関するものである。
The present invention relates to an exhaust gas treating agent containing calcium hydroxide as a main component and a method for producing the same. More specifically, the present invention relates to an exhaust gas treating agent suitable for purifying combustion exhaust gas discharged from an incinerator, a thermal power plant, an electric furnace, and the like of municipal garbage and a method for producing the same.

【0002】[0002]

【従来の技術】水酸化カルシウム(消石灰)は、酸化カ
ルシウム(生石灰)及び水を一定量消化機に供給し、こ
れらを消化機内で混合撹拌して生石灰を消化(水和)す
ることにより製造される。消化機から排出された水酸化
カルシウムは熟成機に供給されて、ここで消化ムラをな
くし、付着水分を均一にした後、排出される。この間に
余分な水分が蒸発し、熟成機の出口で水酸化カルシウム
の水分量が殆どなくなるように消化機に供給される水量
は調節される。水酸化カルシウムの主要な用途の一つと
して、焼却炉等の燃焼排ガスの浄化がある。この排ガス
の浄化に用いられる水酸化カルシウムは排ガス中の塩化
水素や硫黄酸化物との反応性がよいものが望まれてい
る。
2. Description of the Related Art Calcium hydroxide (slaked lime) is produced by supplying a certain amount of calcium oxide (quick lime) and water to a digester, and mixing and stirring them in the digester to digest (hydrate) quick lime. You. The calcium hydroxide discharged from the digester is supplied to the ripening machine, where the unevenness of digestion is eliminated, the attached water is made uniform, and then the calcium hydroxide is discharged. During this time, the amount of water supplied to the digester is adjusted so that excess water evaporates and the amount of calcium hydroxide at the outlet of the ripening machine becomes almost zero. One of the main uses of calcium hydroxide is purification of combustion exhaust gas from incinerators and the like. Calcium hydroxide used for purifying the exhaust gas is desired to have good reactivity with hydrogen chloride and sulfur oxide in the exhaust gas.

【0003】従来、このような用途に向けられた水酸化
カルシウムの製造方法や排ガス処理剤が提案されている
(例えば、特公平6−8194、特開平8−10804
0、特開平9−103640)。特公平6−8194号
公報に記載の発明は、酸化カルシウムと水30〜50容
量部及び低級アルコール、ケトン、エーテル、アルデヒ
ドのような有機溶剤50〜70容量部よりなる消和液体
とを一定の比率で45℃以下の温度で混合し、次いで反
応混合物を主反応容器に移して50〜70℃の温度で反
応させ、最終反応を第2の反応容器内で85〜110℃
の温度で行うことにより乾燥水酸化カルシウムを製造す
る方法である。また特開平8−108040号公報に記
載の発明は、比表面積が25m2/g以上、平均粒子径
が6μm以下、及び反応活性がシュウ酸活性度で30分
以下である水酸化カルシウムからなる排ガス処理剤であ
る。更に特開平9−103640号公報に記載の発明
は、エタノール、メタノール等の低級アルコールを水酸
化カルシウムの0.05〜1.0重量%含有する水酸化
カルシウムを活性分とする排ガス処理剤である。上記公
報に記載の水酸化カルシウム又は排ガス処理剤によれ
ば、いずれも排ガス中の有害な酸化物等を高効率で除去
することができる。ゴミ焼却炉等で発生した燃焼排ガス
を浄化した水酸化カルシウム又は排ガス処理剤は、処理
後に飛灰となり、バグフィルタなどで捕捉された後、セ
メントで固化されて、多くの場合埋立てて処分されてい
る。
Hitherto, a method for producing calcium hydroxide and an exhaust gas treating agent for such a use have been proposed (for example, Japanese Patent Publication No. 6-8194, Japanese Patent Application Laid-Open No. H8-10804).
0, JP-A-9-103640). The invention described in Japanese Patent Publication No. 6-8194 discloses a method in which calcium oxide and a slaking liquid composed of 30 to 50 parts by volume of water and 50 to 70 parts by volume of an organic solvent such as lower alcohol, ketone, ether and aldehyde are fixed. Mix at a temperature below 45 ° C. in a ratio, then transfer the reaction mixture to the main reaction vessel and react at a temperature of 50-70 ° C., and place the final reaction in a second reaction vessel at 85-110 ° C.
This is a method for producing dried calcium hydroxide by performing the above process. The invention described in JP-A-8-108040 discloses an exhaust gas comprising calcium hydroxide having a specific surface area of 25 m 2 / g or more, an average particle diameter of 6 μm or less, and a reaction activity of oxalic acid activity of 30 minutes or less. It is a processing agent. Furthermore, the invention described in JP-A-9-103640 is an exhaust gas treating agent containing calcium hydroxide containing 0.05 to 1.0% by weight of calcium hydroxide of a lower alcohol such as ethanol or methanol and having calcium hydroxide as an active component. . According to the calcium hydroxide or the exhaust gas treating agent described in the above publication, any of them can remove harmful oxides and the like in the exhaust gas with high efficiency. Calcium hydroxide or exhaust gas treatment agent that has purified the combustion exhaust gas generated in garbage incinerators, etc., becomes fly ash after processing, is captured by a bag filter, etc., is solidified with cement, and is often disposed of in landfill. ing.

【0004】特に、特公平6−8194号及び特開平9
−103640号に記載の発明では、低級アルコール等
の有機溶剤を含有させて酸化カルシウムの消化速度を遅
延させることにより、比表面積が高くより反応性の高い
水酸化カルシウムを製造し、排ガス処理効果を高めてい
る。特開平9−103640号に記載の発明は、低級ア
ルコールの含有量を特公平6−8194号に記載の発明
と異ならせることにより、水酸化カルシウムの給排時の
配管の目詰まりや閉塞を防ぎ、貯蔵時の凝集や固結を抑
制する特長がある。
[0004] In particular, Japanese Patent Publication No. 6-8194 and Japanese Patent Application Laid-Open
According to the invention described in JP-A-103640, an organic solvent such as a lower alcohol is contained to delay the digestion rate of calcium oxide, thereby producing a calcium hydroxide having a higher specific surface area and a higher reactivity, and improving the exhaust gas treatment effect. Is increasing. The invention described in Japanese Patent Application Laid-Open No. 9-103640 prevents the clogging and blockage of the pipe during supply and discharge of calcium hydroxide by making the content of the lower alcohol different from the invention described in Japanese Patent Publication No. 6-8194. It has the feature of suppressing aggregation and consolidation during storage.

【0005】[0005]

【発明が解決しようとする課題】しかし、特公平6−8
194号及び特開平9−103640号に記載の発明
は、低級アルコールを含有することに起因して、次の問
題点があった。水酸化カルシウムに含有する低級アル
コールが長時間、高温状態の放置によりアルデヒドに変
成して異臭を生じることがあった。排ガス処理した
後、セメントで固化したときの使用済み水酸化カルシウ
ムはその固化強度が比較的低いため、飛散し易く、処分
しにくかった。水と低級アルコールを混合して消化す
るため、蒸発による脱気の場合、高コストな低級アルコ
ール回収及び再利用装置を必要であった。低級アルコ
ールは揮発性が高く、保管時に火気の取扱いに十分配慮
しなければならなかった。
[Problems to be solved by the invention]
The inventions described in JP-A No. 194 and JP-A-9-103640 have the following problems due to containing a lower alcohol. When a lower alcohol contained in calcium hydroxide is left in a high temperature state for a long time, it may be transformed into an aldehyde to generate an unpleasant odor. After the exhaust gas treatment, the used calcium hydroxide when solidified with cement has a relatively low solidification strength, so that it is easily scattered and difficult to dispose. Since water and lower alcohol are mixed and digested, in the case of degassing by evaporation, a high-cost lower alcohol recovery and reuse device is required. Lower alcohols have high volatility and require careful handling of fire during storage.

【0006】また特開平8−108040号及び特開平
9−103640号に記載の発明では、いずれも水酸化
カルシウムが平均粒子径6μm以下の極めて微細な粒子
であるため、反応性に優れる反面、乾式にて使用する場
合排ガスを処理した後でバグフィルタの濾布に目詰まり
してバグフィルタの圧力損失が増大する等の不都合があ
った。更に排ガス処理剤はスラリー状態にして、排ガス
中に噴霧して使用される場合もあるが、酸化カルシウム
と消化水又は消化アルコール水溶液で作られた排ガス処
理剤のスラリーはその粘性が比較的高く、処理装置の配
管を閉塞する欠点があった。
In the inventions described in JP-A-8-108040 and JP-A-9-103640, calcium hydroxide is an extremely fine particle having an average particle diameter of 6 μm or less. However, when the exhaust gas is treated, the filter cloth of the bag filter is clogged and the pressure loss of the bag filter is increased. Furthermore, the exhaust gas treating agent may be used in the form of a slurry and sprayed into the exhaust gas, but the slurry of the exhaust gas treating agent made of calcium oxide and digested water or digested alcohol aqueous solution has a relatively high viscosity, There was a drawback that the piping of the processing device was blocked.

【0007】本発明の第1の目的は、排ガス中の有害な
酸化物等を高効率で除去する排ガス処理剤及びその製造
方法を提供することにある。本発明の第2の目的は、粉
体の製品になったときの流動性が良好で、また排ガス処
理時のスラリー状態の粘性が低く、それぞれ配管への付
着や閉塞を生じない排ガス処理剤及びその製造方法を提
供することにある。本発明の第3の目的は、保管貯蔵時
に異臭を生じずかつ火気に対して厳重な管理を必要とせ
ず、排ガス処理後のセメント固化したときの強度が高く
処分し易い排ガス処理剤及びその製造方法を提供するこ
とにある。本発明の第4の目的は、排ガス処理後のバグ
フィルタの圧力損失が小さい排ガス処理剤及びその製造
方法を提供することにある。
A first object of the present invention is to provide an exhaust gas treating agent for removing harmful oxides and the like in exhaust gas with high efficiency and a method for producing the same. A second object of the present invention is to provide an exhaust gas treating agent that has good fluidity when it is turned into a powder product, has a low viscosity in a slurry state during exhaust gas treatment, and does not cause adhesion or blockage to pipes, respectively. It is to provide a manufacturing method thereof. A third object of the present invention is to provide an exhaust gas treating agent which does not generate an unpleasant odor during storage and storage, does not require strict control over fire, has high strength when cement solidified after exhaust gas treatment and is easy to dispose, and its production. It is to provide a method. A fourth object of the present invention is to provide an exhaust gas treating agent having a small pressure loss of a bag filter after exhaust gas treatment, and a method for producing the same.

【0008】[0008]

【課題を解決するための手段】請求項1に係る発明は、
水酸化カルシウムを主要成分とし、この水酸化カルシウ
ムに対してヘキシットを0.1〜10重量%含有し、比
表面積が40m2/g以上であり、平均粒径が7〜15
μmである排ガス処理剤である。比表面積が40m2
g以上で高いため、反応性が高く、排ガス中の有害な酸
化物等を高効率で除去する。また平均粒径が7〜15μ
mであって、極めて微細な粒子でないため、排ガス処理
剤は凝集しにくく、かつ排ガス処理後にバグフィルタの
濾布を目詰まりさせない。
The invention according to claim 1 is
It contains calcium hydroxide as a main component, contains 0.1 to 10% by weight of hexite based on the calcium hydroxide, has a specific surface area of 40 m 2 / g or more, and has an average particle size of 7 to 15%.
It is an exhaust gas treating agent having a size of μm. The specific surface area is 40m 2 /
g, it has high reactivity and removes harmful oxides and the like in exhaust gas with high efficiency. The average particle size is 7 to 15μ.
m, which are not very fine particles, so that the exhaust gas treating agent does not easily aggregate and does not clog the filter cloth of the bag filter after exhaust gas treatment.

【0009】請求項2に係る発明は、請求項1に係る発
明であって、無機系鉱物、活性炭類及び軽量気泡コンク
リート廃材からなる群より選ばれた1種又は2種以上の
粉末を水酸化カルシウムに対して1〜50重量%均一に
混合した排ガス処理剤である。平均粒径が7〜15μm
の無機系鉱物、活性炭類、軽量気泡コンクリート廃材か
らなる粉末を水酸化カルシウムに均一に混合することに
より、排ガス処理剤の流動性がより向上し、配管への付
着や閉塞をより一層防止する。
The invention according to claim 2 is the invention according to claim 1, wherein one or more powders selected from the group consisting of inorganic minerals, activated carbons, and lightweight lightweight concrete concrete are hydroxylated. An exhaust gas treating agent uniformly mixed with 1 to 50% by weight of calcium. Average particle size is 7 to 15 μm
By uniformly mixing powder consisting of inorganic minerals, activated carbons, and lightweight aerated concrete waste material with calcium hydroxide, the fluidity of the exhaust gas treating agent is further improved, and adhesion and clogging of pipes are further prevented.

【0010】請求項3に係る発明は、酸化カルシウムと
水とを混合してこの酸化カルシウムを消化させることに
より水酸化カルシウムを製造する方法において、ヘキシ
ットを酸化カルシウムに対して0.1〜10重量%の割
合で酸化カルシウムと混合することを特徴とする排ガス
処理剤の製造方法である。ヘキシットを酸化カルシウム
と混合すると、生成した水酸化カルシウムは微粒子化し
て比表面積が大きくなり、反応性が高くなる。この理由
は、必ずしも明確ではないが、ヘキシットの添加により
生石灰の急激な水和が緩和され、生石灰粒子が水和の際
に粒子表面から徐々に水と反応し、生石灰粒子表面から
微細な消石灰粒子が剥落するように生成するためであろ
うと推察される。更にヘキシットは低級アルコールとは
異なり、酸化カルシウムに対して極めて少量で消化反応
を遅延させる効果がある。この理由は必ずしも明らかで
はないが、以下のように推察される。ヘキシットの添加
により微細な一次粒子を形成するとともに消化水溶液中
の濃度が希薄なため、二次粒子化等が促進され、空隙に
富んだ消石灰の凝集体になる。この凝集体は、粒径が大
きいにも関わらず比表面積も大きく反応性に富みスラリ
ーの粘性を低下させる。更に、微粒子の凝集体であるた
めに微細気孔率が高く、これによりセメント固化強度を
低下させない。
The invention according to claim 3 is a method for producing calcium hydroxide by mixing calcium oxide and water and digesting the calcium oxide, wherein the hexit is 0.1 to 10% by weight based on the calcium oxide. % Of the mixture is mixed with calcium oxide at a ratio of 0.1%. When Hexit is mixed with calcium oxide, the generated calcium hydroxide is finely divided to have a large specific surface area and high reactivity. The reason for this is not always clear, but the addition of hexite alleviates the rapid hydration of quicklime, and the quicklime particles gradually react with water from the particle surface during hydration, and fine slaked lime particles from the surface of the quicklime particles. It is presumed that this is due to the generation of flakes. Furthermore, unlike lower alcohols, hexit has the effect of delaying the digestion reaction with very small amounts of calcium oxide. The reason for this is not necessarily clear, but is presumed as follows. Addition of hexite forms fine primary particles and the concentration in the digestion aqueous solution is low, so that secondary particles are promoted and the like, and agglomerates of slaked lime rich in voids are formed. The agglomerates have a large specific surface area despite their large particle size, are highly reactive, and lower the viscosity of the slurry. In addition, the fine porosity is high due to the aggregate of the fine particles, so that the cement solidification strength is not reduced.

【0011】請求項4に係る発明は、請求項3に係る発
明であって、消化時の雰囲気を減圧する製造方法であ
る。消化時の雰囲気を減圧することにより水の沸点を下
げ、消化反応温度を低くできる。このように消化反応時
の水の沸点が低下し、消化反応温度の最高点が低くなる
ことにより、水酸化カルシウムの比表面積が大きくな
る。請求項5に係る発明は、請求項3又は4に係る発明
であって、消化のための水を2回に分けて酸化カルシウ
ムと混合し、1回目に混合する水にヘキシットを添加
し、2回目に添加する水にアルカリ水酸化物を添加する
製造方法である。2回目に添付する消化水にアルカリ水
酸化物を添加することにより、水酸化カルシウムの結晶
の微粒化が促進され、水酸化カルシウムの比表面積が増
大する。なお、この場合においても、1回目のみ又は1
回目、2回目の双方において雰囲気を減圧しても良い。
The invention according to claim 4 is the invention according to claim 3, which is a manufacturing method in which the atmosphere during digestion is reduced. By reducing the atmosphere during digestion, the boiling point of water can be lowered and the digestion reaction temperature can be lowered. As described above, the boiling point of water at the time of the digestion reaction decreases, and the maximum point of the digestion reaction temperature decreases, whereby the specific surface area of calcium hydroxide increases. The invention according to claim 5 is the invention according to claim 3 or 4, wherein the water for digestion is divided into two portions and mixed with calcium oxide. This is a production method in which an alkali hydroxide is added to water to be added a second time. By adding an alkali hydroxide to the digestion water attached for the second time, the atomization of calcium hydroxide crystals is promoted, and the specific surface area of calcium hydroxide increases. In this case as well, only the first time or 1
The atmosphere may be decompressed both in the second time and the second time.

【0012】請求項6に係る発明は、請求項3ないし5
のいずれかに係る発明であって、消化のための水量を酸
化カルシウムの消化当量の2〜5倍とし、生成した水分
を含む水酸化カルシウムを乾燥させる製造方法である。
このように水を過剰に混合することにより、消化時の温
度が低くなり、消化速度が遅くなる。これにより生成し
た水酸化カルシウムが高活性な状態で空気に接触しにく
くなり、空気中の二酸化炭素や水分の吸収が防止され、
比表面積の高い水酸化カルシウムが得られる。
The invention according to claim 6 is the invention according to claims 3 to 5
The invention according to any one of the above, wherein the amount of water for digestion is 2 to 5 times the digestion equivalent of calcium oxide, and the calcium hydroxide containing generated water is dried.
Such excessive mixing of water lowers the temperature during digestion and slows the digestion rate. The resulting calcium hydroxide is less likely to come into contact with air in a highly active state, preventing the absorption of carbon dioxide and moisture in the air,
Calcium hydroxide having a high specific surface area can be obtained.

【0013】請求項7に係る発明は、請求項3ないし6
のいずれかに係る発明であって、ヘキシット水溶液に水
より沸点の高い有機溶剤をヘキシットに対して5〜40
重量%の割合で添加する製造方法である。水より沸点の
高い有機溶剤を更に含ませることにより、粒子間の付着
力を低減し帯電をも防ぐこととなり、その結果排ガス処
理剤の流動性がより向上し、配管への付着や閉塞をより
一層防止する。
The invention according to claim 7 is the invention according to claims 3 to 6
An organic solvent having a higher boiling point than water is added to the aqueous hexit solution in an amount of 5 to 40 to the hexite.
This is a production method in which the additive is added at a ratio of% by weight. By further including an organic solvent having a boiling point higher than that of water, the adhesion between particles is reduced and electrification is also prevented. As a result, the fluidity of the exhaust gas treating agent is further improved, and the adhesion and clogging of pipes are reduced. Prevent further.

【0014】請求項8に係る発明は、請求項3ないし7
のいずれかに係る発明であて、消化して生成された水酸
化カルシウムに無機系鉱物、活性炭類及び軽量気泡コン
クリート廃材からなる群より選ばれた1種又は2種以上
の平均粒径が7〜15μmの粉末を添加混合する製造方
法である。平均粒径が7〜15μmの無機系鉱物、活性
炭類、軽量気泡コンクリート廃材からなる粉末を水酸化
カルシウムに均一に混合することにより、排ガス処理剤
の流動性がより向上し、配管への付着や閉塞をより一層
防止する。
The invention according to claim 8 is the invention according to claims 3 to 7
The invention according to any one of the above, wherein the calcium hydroxide produced by digestion has an average particle diameter of one or more selected from the group consisting of inorganic minerals, activated carbon, and lightweight aerated concrete waste material of 7 to This is a production method in which 15 μm powder is added and mixed. By uniformly mixing powder composed of inorganic minerals having an average particle diameter of 7 to 15 μm, activated carbons, and lightweight lightweight concrete concrete with calcium hydroxide, the flowability of the exhaust gas treating agent is further improved, Blockage is further prevented.

【0015】[0015]

【発明の実施の形態】本発明で使用される原料の酸化カ
ルシウム(生石灰)は、活性度が高いほど良く、粒度は
微細な程、好ましい。5mm以下、特に150μm以下
であることが好ましい。活性度としては、後述の実施例
において定義される50g法による活性度が250(m
l/5分)以上であることが好ましい。
BEST MODE FOR CARRYING OUT THE INVENTION The raw material calcium oxide (quick lime) used in the present invention is preferably as active as it is higher and finer in particle size. It is preferably 5 mm or less, particularly preferably 150 μm or less. As the activity, the activity by the 50 g method defined in Examples described later is 250 (m
1/5 minutes) or more.

【0016】請求項1及び3に係る発明では、原料の酸
化カルシウムを水で消化する際、ヘキシットを添加す
る。ヘキシットは糖アルコールの一種であり、ヘキソー
スの還元で得られる六価アルコールの総称であり、CH
2OH(CHOH)4CH2OHの構造を有する。本発明で
使用されるヘキシットとしてはD−ソルビット、D−マ
ンニット、D−インジット、D−タリット、ズルシッ
ト、アリットが挙げられる。特に自然界に存在するD−
ソルビット、D−マンニット、D−インジット、ズルシ
ットが好ましい。ヘキシットは、生石灰と消化水との反
応速度を遅延させる効果がある。ヘキシットの添加によ
り、生石灰粒子が水和する際に粒子表面から徐々に水と
反応し、微細な水酸化カルシウム粒子が生成し、これに
より水酸化カルシウムの比表面積が増大するものと推察
される。ヘキシットは酸化カルシウムに対して0.1〜
10重量%の割合で水酸化カルシウムと混合される。好
ましくは0.3〜3重量%、最も好ましくは0.5〜2
重量%添加される。添加量が0.1重量%未満では反応
性の改善が不十分となり、10重量%を超えるとコスト
高となる。ヘキシットの混合の仕方は、水に可溶なヘキ
シットを消化水に加えてヘキシット水溶液にした後、こ
のヘキシット水溶液と生石灰とを混合撹拌するのが好ま
しい。これ以外に、生石灰、消化水及びヘキシットの三
者を別々に混合してもよい。この混合撹拌装置は、撹拌
機付の混合容器でもよいし、連続式のラインミキサーで
もよい。
According to the first and third aspects of the present invention, when digesting calcium oxide as a raw material with water, hexit is added. Hexit is a kind of sugar alcohol, and is a general term for hexahydric alcohol obtained by reduction of hexose, CH
It has the structure of 2 OH (CHOH) 4 CH 2 OH. Hexit used in the present invention includes D-sorbit, D-mannit, D-inject, D-talit, dullcit, and alit. Especially D- which exists in the natural world
Sorbit, D-mannit, D-inject, and dursit are preferred. Hexit has the effect of slowing the rate of reaction between quicklime and digestive water. It is presumed that the addition of hexite causes the lime particles to gradually react with water from the particle surface when hydrated, and to generate fine calcium hydroxide particles, thereby increasing the specific surface area of calcium hydroxide. Hexit is 0.1 to calcium oxide
It is mixed with calcium hydroxide in a proportion of 10% by weight. Preferably 0.3-3% by weight, most preferably 0.5-2%
% By weight. If the added amount is less than 0.1% by weight, the improvement of the reactivity is insufficient, and if it exceeds 10% by weight, the cost increases. It is preferable that the hexit is mixed by adding a hexit soluble in water to digested water to form a hexit aqueous solution, and then mixing and stirring the hexit aqueous solution and quicklime. Alternatively, quicklime, digested water and hexit may be separately mixed. The mixing and stirring device may be a mixing vessel equipped with a stirrer or a continuous line mixer.

【0017】請求項4に係る発明では、消化時の雰囲気
を減圧する。このときの雰囲気圧は0.6気圧以上が好
ましい。請求項5に係る発明では、2回目に添加する水
にアルカリ水酸化物を添加する。このアルカリ水酸化物
としては、水酸化ナトリウム、水酸化カリウム、水酸化
リチウムが挙げられる。このアルカリ水酸化物は酸化カ
ルシウムに対して0.05〜3重量%添加するのが好ま
しい。請求項6に係る発明では、消化のための水量は酸
化カルシウムの消化当量の2〜5倍である。この水量は
好ましくは2.5〜5倍である。また生成した水酸化カ
ルシウム中の水分が3〜30重量%、好ましくは5〜2
0重量%となるように消化水量を決めることが好まし
い。消化水量が理論消化水量の2倍未満或いは生成した
水酸化カルシウムの水分が3重量%未満では比表面積が
小さくなり、反応性の改善が不十分となる。消化水量が
理論消化水量の5倍を超え、生成した水酸化カルシウム
の水分が30重量%を超えると、水酸化カルシウムがペ
ースト状ないしスラリー状となり、別個に脱水装置が必
要となる。なお、消化時の温度を下げるために理論量の
2〜5倍の水を添加する以外に、強制的に消化雰囲気温
度を下げても良い。消化時の温度は100℃以下、好ま
しくは80℃以下である。
In the invention according to claim 4, the atmosphere during digestion is reduced in pressure. Atmospheric pressure at this time is preferably at least 0.6 atm. In the invention according to claim 5, an alkali hydroxide is added to the water to be added for the second time. Examples of the alkali hydroxide include sodium hydroxide, potassium hydroxide, and lithium hydroxide. This alkali hydroxide is preferably added in an amount of 0.05 to 3% by weight based on calcium oxide. In the invention according to claim 6, the amount of water for digestion is 2 to 5 times the digestive equivalent of calcium oxide. This amount of water is preferably 2.5 to 5 times. Further, the water content in the generated calcium hydroxide is 3 to 30% by weight, preferably 5 to 2%.
It is preferable to determine the amount of digested water so as to be 0% by weight. If the amount of digested water is less than twice the theoretical amount of digested water or the generated calcium hydroxide has a water content of less than 3% by weight, the specific surface area becomes small, and the improvement of reactivity becomes insufficient. When the amount of digested water exceeds 5 times the theoretical amount of digested water and the water content of the generated calcium hydroxide exceeds 30% by weight, the calcium hydroxide becomes a paste or slurry, and a separate dehydrator is required. In addition, in addition to adding 2 to 5 times the theoretical amount of water to lower the temperature during digestion, the digestive atmosphere temperature may be forcibly reduced. The temperature during digestion is 100 ° C or lower, preferably 80 ° C or lower.

【0018】請求項7に係る発明では、ヘキシット水溶
液に水より沸点の高い有機溶剤をヘキシットに対して5
〜100重量%の割合で添加する。この有機溶剤として
はエチレングリコール、ジエチレングリコール、トリエ
チレングリコール、ポリエチレングリコール、グリセリ
ン等が挙げられる。この添加量は好ましくは10〜80
重量%、更に好ましくは20〜60重量%である。5重
量%未満では添加する効果に乏しく、100重量%を超
えると極めて微細な水酸化カルシウム粉が多量に発生す
るため、平均粒径を大きく下げ目標である平均粒径7〜
15μmを製造しにくくなり、更にコスト高となる。請
求項2及び8に係る発明では、無機系鉱物、活性炭類及
び軽量気泡コンクリート廃材からなる群より選ばれた1
種又は2種以上の粉末を水酸化カルシウムに対して1〜
50重量%均一に混合する。無機系鉱物としてはゼオラ
イト、活性白土、パーライト、クレー等が挙げられ、活
性炭類としては活性炭、間伐材、建築廃材、籾殻等が挙
げられる。
In the invention according to claim 7, an organic solvent having a boiling point higher than that of water is added to the aqueous hexit solution in an amount of 5 to hexit.
100100% by weight. Examples of the organic solvent include ethylene glycol, diethylene glycol, triethylene glycol, polyethylene glycol, glycerin and the like. This addition amount is preferably 10 to 80
%, More preferably 20 to 60% by weight. If the amount is less than 5% by weight, the effect of addition is poor, and if it exceeds 100% by weight, a large amount of extremely fine calcium hydroxide powder is generated.
It becomes difficult to manufacture the 15 μm, and the cost is further increased. In the invention according to claims 2 and 8, one selected from the group consisting of inorganic minerals, activated carbons and lightweight aerated concrete wastes.
Seed or two or more powders with respect to calcium hydroxide
Mix 50% by weight uniformly. Inorganic minerals include zeolite, activated clay, perlite, clay, and the like. Activated carbons include activated carbon, thinned wood, construction waste, rice hulls, and the like.

【0019】消化反応で生成した水分を含む水酸化カル
シウム(消石灰)は、熟成機内に導入され、撹拌羽根に
よって撹拌され、熟成される。熟成された消石灰は、乾
燥機に導入され、撹拌羽根で撹拌され、乾燥される。そ
の後、分級機で所定の粒度以下に分級し、粗粉は粉砕機
で粉砕し、製品とする。なお、熟成機を省略し、消石灰
を消化機から直接に乾燥機へ供給することも可能であ
る。乾燥機としては、バドルドライヤー、ベルト乾燥
機、バンド乾燥機、ロータリー乾燥機、流動乾燥機、気
流乾燥機、電磁波乾燥機、赤外(遠赤外)乾燥機が挙げ
られる。好ましくは、できるだけ炭酸ガスとの接触を避
け、水酸化カルシウムが炭酸化して炭酸カルシウムにな
ることを避けるため、間接加熱式のものが使用される。
Calcium hydroxide (slaked lime) containing water generated by the digestion reaction is introduced into a ripening machine, and is aged by being stirred by stirring blades. The aged slaked lime is introduced into a dryer, stirred by a stirring blade, and dried. Thereafter, the powder is classified to a predetermined particle size or less by a classifier, and the coarse powder is pulverized by a pulverizer to obtain a product. It is also possible to omit the aging machine and supply slaked lime directly from the digester to the dryer. Examples of the dryer include a paddle dryer, a belt dryer, a band dryer, a rotary dryer, a fluid dryer, a flash dryer, an electromagnetic wave dryer, and an infrared (far infrared) dryer. Preferably, an indirect heating type is used in order to avoid contact with carbon dioxide gas as much as possible and to prevent calcium hydroxide from being carbonated into calcium carbonate.

【0020】上記方法では、比表面積40m2/g以上
で、平均粒径15μm以下の水酸化カルシウムが得られ
る。本発明ではこの水酸化カルシウムを篩分して、この
うち平均粒径が7μm以上の水酸化カルシウムを排ガス
処理剤とする。極めて微細な粒径の水酸化カルシウムは
排ガス処理後のバグフィルタの濾布の目詰まりの原因と
なるからである。また平均粒径が7〜15μmの水酸化
カルシウムは、微粒子化しているため、白色度が90以
上となり、見栄えが良く、製品価値が高まる。また安息
角が50度以下と小さくなり、流動性に優れる。従って
この排ガス処理剤は配管やホッパー等への付着少なく、
ホッパーからの抜き出しが容易である。
According to the above method, calcium hydroxide having a specific surface area of 40 m 2 / g or more and an average particle size of 15 μm or less can be obtained. In the present invention, this calcium hydroxide is sieved, and calcium hydroxide having an average particle diameter of 7 μm or more is used as an exhaust gas treating agent. This is because calcium hydroxide having an extremely fine particle size causes clogging of the filter cloth of the bag filter after exhaust gas treatment. Further, calcium hydroxide having an average particle size of 7 to 15 μm is finely divided, so that the whiteness is 90 or more, the appearance is good, and the product value is enhanced. In addition, the angle of repose is as small as 50 degrees or less, and the fluidity is excellent. Therefore, this exhaust gas treatment agent adheres little to pipes and hoppers,
Extraction from the hopper is easy.

【0021】[0021]

【実施例】次に本発明の具体的態様を示すために、本発
明の実施例を比較例とともに説明する。以下の実施例及
び比較例では、原料の酸化カルシウムとして粒径150
μm以下、活性度310(ml/5分)の生石灰粉末を
用いた。この活性度とは、3リットルのビーカーに水2
リットル(40℃)を入れ撹拌を行い、生石灰50g
(粒度10〜3mm)を投入すると同時に指示薬のフェ
ノールフタレインを2〜3滴滴下する。溶液が僅かに赤
色を持続するように4N−HClを継続して5分間滴下
する。このときの塩酸消費量を活性度と定義する。塩酸
消費量が多いほど活性度が高いことを示す。
EXAMPLES Next, examples of the present invention will be described together with comparative examples in order to show specific embodiments of the present invention. In the following Examples and Comparative Examples, as a raw material calcium oxide, a particle size of 150 was used.
Quicklime powder having an activity of 310 μm or less (ml / 5 min) was used. This activity refers to a 3 liter beaker with 2 water
Liter (40 ° C.) and stir, then 50 g of quicklime
(Particle size: 10 to 3 mm), and at the same time, 2 to 3 drops of phenolphthalein as an indicator are dropped. 4N-HCl is continuously added dropwise for 5 minutes so that the solution remains slightly red. The hydrochloric acid consumption at this time is defined as activity. The higher the consumption of hydrochloric acid, the higher the activity.

【0022】<実施例1>D−ソルビット30gを20
℃の水9.6kgに溶解し、このソルビット水溶液を用
いて10kgの生石灰を消化した。従って、ソルビット
の添加量は、生石灰に対し0.3重量%である。また、
消化水量は理論量の3倍である。消化時の雰囲気圧力は
1気圧(大気圧)とし、雰囲気温度は10℃とした。1
時間熟成後の水分(乾燥前)は18.6%であった。こ
れを乾燥して水酸化カルシウムを主要成分とする排ガス
処理剤を製造した。乾燥後の水分は0.2%であった。 <実施例2>D−ソルビット添加量を0.5重量%、消
化水量を理論値の2.5倍、1時間熟成後の水分(乾燥
前)を10.2%、乾燥後の水分を0.1%とした以外
は実施例1と同様にして水酸化カルシウムを主要成分と
する排ガス処理剤を製造した。
<Embodiment 1> 30 g of D-sorbit was added to 20 g
The solution was dissolved in 9.6 kg of water at ℃, and 10 kg of quicklime was digested using this sorbite aqueous solution. Therefore, the addition amount of sorbite is 0.3% by weight based on quicklime. Also,
The amount of digested water is three times the theoretical amount. The atmospheric pressure during digestion was 1 atm (atmospheric pressure), and the atmospheric temperature was 10 ° C. 1
The water content (before drying) after the time aging was 18.6%. This was dried to produce an exhaust gas treating agent containing calcium hydroxide as a main component. The water content after drying was 0.2%. <Example 2> The amount of D-sorbitol added was 0.5% by weight, the amount of digested water was 2.5 times the theoretical value, the moisture after aging for 1 hour (before drying) was 10.2%, and the moisture after drying was 0%. An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the amount was 0.1%.

【0023】<実施例3>D−ソルビット添加量を0.
5重量%とした以外は実施例1と同様にして水酸化カル
シウムを主要成分とする排ガス処理剤を製造した。 <実施例4>D−ソルビット添加量を0.5重量%、消
化水量を理論値の5倍、1時間熟成後の水分(乾燥前)
を48.7%、乾燥後の水分を0.5%とした以外は実
施例1と同様にして水酸化カルシウムを主要成分とする
排ガス処理剤を製造した。 <実施例5>D−ソルビット添加量を0.5重量%、消
化水量を理論値の7倍、1時間熟成後の水分(乾燥前)
を104.3%、乾燥後の水分を8.6%とした以外は
実施例1と同様にして水酸化カルシウムを主要成分とす
る排ガス処理剤を製造した。
<Embodiment 3> The amount of D-sorbitol added was set to 0.
Except that the content was 5% by weight, an exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1. <Example 4> The amount of D-sorbitol added was 0.5% by weight, the amount of digested water was 5 times the theoretical value, and the moisture after aging for 1 hour (before drying)
Was 48.7% and the moisture after drying was 0.5%, to produce an exhaust gas treating agent containing calcium hydroxide as a main component in the same manner as in Example 1. <Example 5> The amount of D-sorbitol added was 0.5% by weight, the amount of digested water was 7 times the theoretical value, and the water content after aging for 1 hour (before drying)
And an exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the water content after drying was changed to 104.3% and the water content after drying was changed to 8.6%.

【0024】<実施例6>D−ソルビット添加量を1.
0重量%、1時間熟成後の水分(乾燥前)を18.1%
とした以外は実施例1と同様にして水酸化カルシウムを
主要成分とする排ガス処理剤を製造した。 <実施例7>D−ソルビット添加量を2.0重量%、1
時間熟成後の水分(乾燥前)を18.8%とした以外は
実施例1と同様にして水酸化カルシウムを主要成分とす
る排ガス処理剤を製造した。 <実施例8>D−ソルビット添加量を6.0重量%、1
時間熟成後の水分(乾燥前)を18.8%とした以外は
実施例1と同様にして水酸化カルシウムを主要成分とす
る排ガス処理剤を製造した。
<Embodiment 6> The amount of D-sorbitol added was set to 1.
0% by weight, moisture after 1 hour aging (before drying) 18.1%
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the above conditions were used. <Example 7> The amount of D-sorbitol added was 2.0% by weight,
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the moisture after aging (before drying) was changed to 18.8%. Example 8 The amount of D-sorbitol added was 6.0% by weight,
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the moisture after aging (before drying) was changed to 18.8%.

【0025】<実施例9>D−ソルビット添加量を1
0.0重量%、1時間熟成後の水分(乾燥前)を28.
9%、乾燥後の水分を0.3%とした以外は実施例1と
同様にして水酸化カルシウムを主要成分とする排ガス処
理剤を製造した。 <実施例10>D−ソルビット添加量を0.5重量%、
消化時の雰囲気圧力を0.6気圧、1時間熟成後の水分
(乾燥前)を15.9%とした以外は実施例1と同様に
して水酸化カルシウムを主要成分とする排ガス処理剤を
製造した。 <実施例11>D−ソルビット添加量を0.5重量%、
消化時の雰囲気圧力を0.8気圧、1時間熟成後の水分
(乾燥前)を17.1%とした以外は実施例1と同様に
して水酸化カルシウムを主要成分とする排ガス処理剤を
製造した。
<Embodiment 9> The amount of D-sorbit added was 1
28. Water content (before drying) after aging for 1 hour at 0.0% by weight.
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the water content after drying was 9% and the moisture content after drying was 0.3%. <Example 10> The amount of D-sorbitol added was 0.5% by weight,
Manufacture of an exhaust gas treating agent containing calcium hydroxide as a main component in the same manner as in Example 1 except that the atmospheric pressure during digestion was changed to 0.6 atm and the moisture after aging for 1 hour (before drying) was changed to 15.9%. did. <Example 11> The amount of D-sorbitol added was 0.5% by weight,
Manufacture of an exhaust gas treating agent containing calcium hydroxide as a main component in the same manner as in Example 1 except that the atmospheric pressure during digestion was set to 0.8 atm and the moisture after aging for 1 hour (before drying) was set to 17.1%. did.

【0026】<実施例12>消化水を2回に分けて添加
した。1回目に理論量の2倍を添加し、2回目に理論量
と同量を添加した。D−ソルビット添加量を0.5重量
%、1時間熟成後の水分(乾燥前)を18.1%とした
以外は実施例1と同様にして水酸化カルシウムを主要成
分とする排ガス処理剤を製造した。 <実施例13>消化水を2回に分けて添加した。1回目
に理論量と同量を添加し、2回目に理論量の2倍を添加
した。2回目の消化水にNaOH水溶液を加えた。Na
OH量は生石灰に対して0.1重量%であった。D−ソ
ルビット添加量を0.5重量%、1時間熟成後の水分
(乾燥前)を19.6%とした以外は実施例1と同様に
して水酸化カルシウムを主要成分とする排ガス処理剤を
製造した。
Example 12 Digested water was added in two portions. Twice the theoretical amount was added the first time, and the same amount as the theoretical amount was added the second time. An exhaust gas treating agent containing calcium hydroxide as a main component was prepared in the same manner as in Example 1 except that the amount of D-sorbitol added was 0.5% by weight and the moisture after aging for 1 hour (before drying) was 18.1%. Manufactured. Example 13 Digestion water was added in two portions. The first time, the same amount as the theoretical amount was added, and the second time, twice the theoretical amount was added. An aqueous NaOH solution was added to the second digestion water. Na
The OH content was 0.1% by weight based on quicklime. An exhaust gas treating agent containing calcium hydroxide as a main component was prepared in the same manner as in Example 1 except that the amount of D-sorbitol added was 0.5% by weight and the moisture after aging for 1 hour (before drying) was 19.6%. Manufactured.

【0027】<実施例14>消化水を2回に分けて添加
した。1回目に理論量の2倍を添加し、2回目に理論量
と同量を添加した。2回目の消化水にNaOH水溶液を
加えた。NaOH量は生石灰に対して0.1重量%であ
った。D−ソルビット添加量を0.5重量%、1時間熟
成後の水分(乾燥前)を22.8%とした以外は実施例
1と同様にして水酸化カルシウムを主要成分とする排ガ
ス処理剤を製造した。 <実施例15>消化水を2回に分けて添加した。1回目
に理論量の2.5倍を添加し、2回目に理論量の0.5
倍を添加した。2回目の消化水にNaOH水溶液を加え
た。NaOH量は生石灰に対して0.1重量%であっ
た。D−ソルビット添加量を0.5重量%、1時間熟成
後の水分(乾燥前)を31.6%とした以外は実施例1
と同様にして水酸化カルシウムを主要成分とする排ガス
処理剤を製造した。
Example 14 Digested water was added in two portions. Twice the theoretical amount was added the first time, and the same amount as the theoretical amount was added the second time. An aqueous NaOH solution was added to the second digestion water. The amount of NaOH was 0.1% by weight based on quicklime. An exhaust gas treating agent containing calcium hydroxide as a main component was prepared in the same manner as in Example 1 except that the amount of D-sorbitol added was 0.5% by weight, and the moisture after aging for 1 hour (before drying) was 22.8%. Manufactured. Example 15 Digested water was added in two portions. The first time, 2.5 times the theoretical amount was added, and the second time, 0.5 times the theoretical amount.
One-fold was added. An aqueous NaOH solution was added to the second digestion water. The amount of NaOH was 0.1% by weight based on quicklime. Example 1 except that the amount of D-sorbitol added was 0.5% by weight and the moisture after aging for 1 hour (before drying) was 31.6%.
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as described above.

【0028】<実施例16>消化水を2回に分けて添加
した。1回目に理論量の2倍を添加し、2回目に理論量
と同量を添加した。2回目の消化水にNaOH水溶液を
加えた。NaOH量は生石灰に対して0.1重量%であ
った。D−ソルビット添加量を0.5重量%、消化時の
雰囲気圧力を0.6気圧、1時間熟成後の水分(乾燥
前)を21.8%とした以外は実施例1と同様にして水
酸化カルシウムを主要成分とする排ガス処理剤を製造し
た。 <実施例17>消化水を2回に分けて添加した。1回目
に理論量の2倍を添加し、2回目に理論量と同量を添加
した。2回目の消化水にNaOH水溶液を加えた。Na
OH量は生石灰に対して0.1重量%であった。D−ソ
ルビット添加量を0.5重量%、消化時の雰囲気圧力を
0.8気圧、1時間熟成後の水分(乾燥前)を22.8
%、乾燥後の水分を0.3%とした以外は実施例1と同
様にして水酸化カルシウムを主要成分とする排ガス処理
剤を製造した。
Example 16 Digested water was added in two portions. Twice the theoretical amount was added the first time, and the same amount as the theoretical amount was added the second time. An aqueous NaOH solution was added to the second digestion water. The amount of NaOH was 0.1% by weight based on quicklime. Water was prepared in the same manner as in Example 1 except that the amount of D-sorbitol added was 0.5% by weight, the atmospheric pressure during digestion was 0.6 atm, and the moisture after aging (before drying) was 21.8%. An exhaust gas treating agent containing calcium oxide as a main component was manufactured. <Example 17> Digested water was added in two portions. Twice the theoretical amount was added the first time, and the same amount as the theoretical amount was added the second time. An aqueous NaOH solution was added to the second digestion water. Na
The OH content was 0.1% by weight based on quicklime. The amount of D-sorbitol added was 0.5% by weight, the atmospheric pressure during digestion was 0.8 atm, and the moisture after aging for 1 hour (before drying) was 22.8.
%, And an exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the water content after drying was changed to 0.3%.

【0029】<比較例1>消化水にヘキシットを全く添
加しなかった。消化水量を理論値の2倍、1時間熟成後
の水分(乾燥前)を0.1%、乾燥後の水分を0.1%
とした以外は実施例1と同様にして水酸化カルシウムを
主要成分とする排ガス処理剤を製造した。 <比較例2>消化水にヘキシットを全く添加しなかっ
た。1時間熟成後の水分(乾燥前)を13.5%、乾燥
後の水分を0.1%とした以外は実施例1と同様にして
水酸化カルシウムを主要成分とする排ガス処理剤を製造
した。 <比較例3>消化水にヘキシットを全く添加しなかっ
た。消化水量を理論値の5倍、1時間熟成後の水分(乾
燥前)を30.7%、乾燥後の水分を0.3%とした以
外は実施例1と同様にして水酸化カルシウムを主要成分
とする排ガス処理剤を製造した。
Comparative Example 1 No hexit was added to digested water. The digested water amount is twice the theoretical value, the moisture after aging for 1 hour (before drying) is 0.1%, and the moisture after drying is 0.1%
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the above conditions were used. <Comparative Example 2> No hexit was added to digested water. An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the moisture after aging for 1 hour (before drying) was 13.5% and the moisture after drying was 0.1%. . Comparative Example 3 No hexit was added to digested water. Calcium hydroxide was mainly used in the same manner as in Example 1 except that the digested water amount was 5 times the theoretical value, the moisture after aging for 1 hour (before drying) was 30.7%, and the moisture after drying was 0.3%. An exhaust gas treating agent as a component was produced.

【0030】<比較例4>消化水にヘキシットを全く添
加しなかった。消化水量を理論値の7倍、1時間熟成後
の水分(乾燥前)を85.3%、乾燥後の水分を5.6
%とした以外は実施例1と同様にして水酸化カルシウム
を主要成分とする排ガス処理剤を製造した。 <比較例5>消化水にヘキシットを全く添加しなかっ
た。消化時の雰囲気圧力を0.6気圧、1時間熟成後の
水分(乾燥前)を12.7%、乾燥後の水分を0.1%
とした以外は実施例1と同様にして水酸化カルシウムを
主要成分とする排ガス処理剤を製造した。 <比較例6>消化水にヘキシットを全く添加しなかっ
た。また消化水を2回に分けて添加した。1回目に理論
量の2倍を添加し、2回目に理論量と同量を添加した。
1時間熟成後の水分(乾燥前)を12.8%、乾燥後の
水分を0.1%とした以外は実施例1と同様にして水酸
化カルシウムを主要成分とする排ガス処理剤を製造し
た。
Comparative Example 4 No hexit was added to digested water. The digested water amount is 7 times the theoretical value, the moisture after aging for 1 hour (before drying) is 85.3%, and the moisture after drying is 5.6%.
%, An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1. <Comparative Example 5> No hexit was added to digested water. The atmospheric pressure during digestion is 0.6 atm, the moisture after aging for 1 hour (before drying) is 12.7%, and the moisture after drying is 0.1%
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the above conditions were used. <Comparative Example 6> No hexit was added to digested water. Digestion water was added in two portions. Twice the theoretical amount was added the first time, and the same amount as the theoretical amount was added the second time.
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the moisture after aging for 1 hour (before drying) was 12.8% and the moisture after drying was 0.1%. .

【0031】<比較試験1>実施例1〜17及び比較例
1〜6で得られた排ガス処理剤について、白色度、安息
角、比表面積、CAA、平均粒径及び圧力損失を測定し
た。その結果を表1に示す。白色度は、東京電色製カラ
ーエースを用いて測定した。白色度は数値が大きいほど
白いことを意味する。安息角は、ホソカワミクロン製パ
ウダーテスターを用いて測定した。流動性の良い粉体で
は安息角は小さい値を示す。付着凝集性の強い微粉では
安息角は大きな値を示し、流動性は悪くなる傾向にあ
る。比表面積は、比表面測定装置(ユアサ アイオニク
ス社製)を用いて測定した。比表面積は数値が大きいほ
ど粒度が微細なことを意味する。またCAAはクエン酸
活性度の略称である。このCAAは、0.4Nクエン酸
溶液100ml(30℃)を撹拌しながら水酸化カルシ
ウム3.705gを投入し、フェノールフタレインを指
示薬として、液が微紅色から濃赤色に変色するまでの時
間(秒)を測定した値である。このCAA値の小さいも
のほど反応性が高い。更に圧力損失は、ポリエステル製
フェルトからなるバグフィルタ用の濾布を用いて、この
濾布に排ガス処理剤を含塵濃度10g/Nm3で2m3
分の風量になるようにブロワを調整して試験を行い、定
常状態となった時点でのバグフィルタ入口の圧力とその
出口の圧力との差より求めた。
<Comparative Test 1> The exhaust gas treating agents obtained in Examples 1 to 17 and Comparative Examples 1 to 6 were measured for whiteness, angle of repose, specific surface area, CAA, average particle diameter and pressure loss. Table 1 shows the results. The whiteness was measured using Tokyo Denshoku Color Ace. Whiteness means that the larger the numerical value is, the whiter it is. The angle of repose was measured using a Hosokawa Micron powder tester. The angle of repose shows a small value in a powder having good fluidity. The angle of repose of a fine powder having strong adhesion and cohesion tends to be large, and the fluidity tends to be poor. The specific surface area was measured using a specific surface measuring device (manufactured by Yuasa Ionics). The larger the specific surface area, the finer the particle size. CAA is an abbreviation for citric acid activity. This CAA is charged with 3.705 g of calcium hydroxide while stirring 100 ml of a 0.4N citric acid solution (30 ° C.), and the time until the liquid changes from a faint red to a deep red using phenolphthalein as an indicator ( Second). The smaller the CAA value, the higher the reactivity. Further, the pressure loss was measured using a filter cloth for bag filter made of polyester felt, and an exhaust gas treating agent was added to the filter cloth at a dust-containing concentration of 10 g / Nm 3 at 2 m 3 / cm 2.
The test was carried out by adjusting the blower so that the air flow per minute was obtained, and it was determined from the difference between the pressure at the inlet of the bag filter and the pressure at the outlet at the time of the steady state.

【0032】[0032]

【表1】 [Table 1]

【0033】表1から明らかな通り、実施例1〜17で
得られた排ガス処理剤は、白色度が高く、安息角が小さ
く流動性に優れ、比表面積が大きく、しかも反応性が高
かった(CAAの値が低かった)。一方、消化水にヘキ
シットを添加していない比較例1〜6で得られた排ガス
処理剤では、いずれも白色度が低く、安息角が大きく、
比表面積が小さく、反応性も低かった(CAAの値が高
かった)。なお、消化水量が理論量の2倍であるとき、
比表面積はやや小さく、消化水量が6倍以上であると水
酸化カルシウムがペースト状ないしスラリー状となり、
別個に脱水装置が必要となるため、消化水量は2.5〜
5倍とするのが好ましいことが分った。また、消化水を
2回に分けて添加する場合、1回目の水量を2回目より
も多くした方がよいことが実施例13〜15より認めら
れた。
As is clear from Table 1, the exhaust gas treating agents obtained in Examples 1 to 17 had high whiteness, small angle of repose, excellent fluidity, large specific surface area, and high reactivity ( CAA value was low). On the other hand, in the exhaust gas treating agents obtained in Comparative Examples 1 to 6 in which hexit was not added to digested water, the whiteness was low, the angle of repose was large, and
The specific surface area was small and the reactivity was low (the value of CAA was high). When the amount of digested water is twice the theoretical amount,
When the specific surface area is rather small, and the digested water volume is 6 times or more, calcium hydroxide becomes a paste or slurry,
Since a separate dehydrator is required, the digested water volume is 2.5 to
It has been found that it is preferable to make it five times. In addition, when adding the digestion water in two portions, Examples 13 to 15 confirmed that it is better to increase the amount of water in the first time than in the second time.

【0034】2回目の消化水にNaOHを添加すること
により、比表面積が増大し反応性も高くなることが実施
例12〜17の対比より分った。消化時の圧力を減圧す
ることにより比表面積及び反応性が高くなることが実施
例3、10、11と、実施例14、16、17との対比
より分った。なお、消化時の最高温度を測定したところ
次の通りであり、減圧により最高温度が低くなることが
分った。
It was found from the comparison of Examples 12 to 17 that the specific surface area was increased and the reactivity was increased by adding NaOH to the digestion water for the second time. The comparison between Examples 3, 10, and 11 and Examples 14, 16, and 17 shows that the specific surface area and the reactivity are increased by reducing the pressure during digestion. The maximum temperature during digestion was measured as follows, and it was found that the maximum temperature was reduced by reducing the pressure.

【0035】 実施例3 (1気圧) 99℃ 実施例10(0.6気圧) 71℃ 実施例11(0.8気圧) 82℃ 消化水を2度に分け、2回目の消化水にNaOHを添加
し、かつこのときの雰囲気を減圧することにより、比表
面積及び反応性が一段と向上することが実施例12、及
び14、16、17の対比より分った。
Example 3 (1 atm) 99 ° C. Example 10 (0.6 atm) 71 ° C. Example 11 (0.8 atm) 82 ° C. Digestion water is divided into two parts and NaOH is added to the second digestion water. It was found from the comparison of Examples 12, 14, 14, 16 and 17 that the specific surface area and the reactivity were further improved by adding and reducing the atmosphere at this time.

【0036】更に、平均粒径に関しては、ヘキシットを
添加すると大きくなり過剰にヘキシットや水を加えた場
合のみ小さくなる。一方ヘキシットを添加しない比較例
1〜6で得られた排ガス処理剤の平均粒子径は小さくな
り消化水量を増加するほど特に小さくなることが分っ
た。同様に、圧力損失に関しては、ヘキシットを添加す
ると小さくなり過剰にヘキシットや水を加えた場合のみ
大きくなる。一方ヘキシットを添加しない比較例1〜6
で得られた排ガス処理剤の圧力損失は大きくなり消化水
量を増加するほど特に大きくなることが分った。
Further, the average particle size increases when hexite is added, and decreases only when hexite or water is excessively added. On the other hand, it was found that the average particle diameter of the exhaust gas treating agents obtained in Comparative Examples 1 to 6 in which hexit was not added became smaller and became particularly smaller as the amount of digested water increased. Similarly, the pressure loss decreases when hexite is added and increases only when hexite or water is excessively added. On the other hand, Comparative Examples 1 to 6 without addition of hexite
It has been found that the pressure loss of the exhaust gas treating agent obtained in (1) becomes large and becomes particularly large as the amount of digested water increases.

【0037】<実施例18>D−ソルビット添加量を
0.5重量%とした以外は実施例1と同様にして水酸化
カルシウムを主要成分とする排ガス処理剤を製造した。 <実施例19>D−マンニット添加量を0.5重量%と
した以外は実施例1と同様にして水酸化カルシウムを主
要成分とする排ガス処理剤を製造した。 <実施例20>ズルシット添加量を0.5重量%とした
以外は実施例1と同様にして水酸化カルシウムを主要成
分とする排ガス処理剤を製造した。
Example 18 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the amount of D-sorbitol was changed to 0.5% by weight. <Example 19> An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the amount of D-mannitol added was 0.5% by weight. <Example 20> An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the added amount of dursit was 0.5% by weight.

【0038】<実施例21>D−ソルビット添加量を
1.0重量%とした以外は実施例1と同様にして水酸化
カルシウムを主要成分とする排ガス処理剤を製造した。 <実施例22>D−マンニット添加量を1.0重量%と
した以外は実施例1と同様にして水酸化カルシウムを主
要成分とする排ガス処理剤を製造した。 <実施例23>ズルシット添加量を1.0重量%とした
以外は実施例1と同様にして水酸化カルシウムを主要成
分とする排ガス処理剤を製造した。
Example 21 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the amount of D-sorbite was changed to 1.0% by weight. <Example 22> An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the amount of D-mannitol was changed to 1.0% by weight. Example 23 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that the added amount of dursit was 1.0% by weight.

【0039】<実施例24>D−ソルビットを1.0重
量%とジエチレングリコールを0.1重量%添加した以
外は実施例1と同様にして水酸化カルシウムを主要成分
とする排ガス処理剤を製造した。 <実施例25>D−ソルビットを1.0重量%とジエチ
レングリコールを0.3重量%添加した以外は実施例1
と同様にして水酸化カルシウムを主要成分とする排ガス
処理剤を製造した。 <実施例26>D−ソルビットを1.0重量%とグリセ
リンを0.1重量%添加した以外は実施例1と同様にし
て水酸化カルシウムを主要成分とする排ガス処理剤を製
造した。
Example 24 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1, except that 1.0% by weight of D-sorbitol and 0.1% by weight of diethylene glycol were added. . <Example 25> Example 1 except that 1.0% by weight of D-sorbitol and 0.3% by weight of diethylene glycol were added.
An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as described above. Example 26 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 1.0% by weight of D-sorbitol and 0.1% by weight of glycerin were added.

【0040】<実施例27>D−ソルビットを1.0重
量%とグリセリンを0.3重量%添加した以外は実施例
1と同様にして水酸化カルシウムを主要成分とする排ガ
ス処理剤を製造した。 <実施例28>D−ソルビットを1.0重量%とゼオラ
イトを2重量%添加した以外は実施例1と同様にして水
酸化カルシウムを主要成分とする排ガス処理剤を製造し
た。 <実施例29>D−ソルビットを1.0重量%とゼオラ
イトを4重量%添加した以外は実施例1と同様にして水
酸化カルシウムを主要成分とする排ガス処理剤を製造し
た。
Example 27 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 1.0% by weight of D-sorbitol and 0.3% by weight of glycerin were added. . Example 28 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 1.0% by weight of D-sorbite and 2% by weight of zeolite were added. Example 29 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 1.0% by weight of D-sorbite and 4% by weight of zeolite were added.

【0041】<実施例30>D−ソルビットを1.0重
量%と活性白土を2重量%添加した以外は実施例1と同
様にして水酸化カルシウムを主要成分とする排ガス処理
剤を製造した。 <実施例31>D−ソルビットを1.0重量%と活性白
土を4重量%添加した以外は実施例1と同様にして水酸
化カルシウムを主要成分とする排ガス処理剤を製造し
た。
Example 30 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 1.0% by weight of D-sorbite and 2% by weight of activated clay were added. <Example 31> An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 1.0% by weight of D-sorbite and 4% by weight of activated clay were added.

【0042】<比較例7>消化水にヘキシットを全く添
加しなかった以外は実施例1と同様にして水酸化カルシ
ウムを主要成分とする排ガス処理剤を製造した。 <比較例8>エタノールを30重量%添加した以外は実
施例1と同様にして水酸化カルシウムを主要成分とする
排ガス処理剤を製造した。 <比較例9>エタノールを40重量%添加した以外は実
施例1と同様にして水酸化カルシウムを主要成分とする
排ガス処理剤を製造した。
Comparative Example 7 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that no hexite was added to digested water. Comparative Example 8 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 30% by weight of ethanol was added. Comparative Example 9 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that ethanol was added at 40% by weight.

【0043】<比較例10>エタノールを50重量%添
加した以外は実施例1と同様にして水酸化カルシウムを
主要成分とする排ガス処理剤を製造した。
Comparative Example 10 An exhaust gas treating agent containing calcium hydroxide as a main component was produced in the same manner as in Example 1 except that 50% by weight of ethanol was added.

【0044】<比較試験2>実施例18〜31及び比較
例7〜9で得られた排ガス処理剤について、平均粒径、
白色度、安息角、比表面積、スラリー粘性、セメント固
化強度及び圧力損失を測定した。その結果を表2に示
す。平均粒径、白色度、安息角、比表面積及び圧力損失
は前述した比較試験1と同様に測定した。スラリー粘性
は、得られた排ガス処理剤を水と混合して濃度30%の
スラリーを調製し、このスラリーの粘性をB型粘度計に
より測定した。値が小さいほど低い粘性を示す。セメン
ト固化強度は、得られた排ガス処理剤を用いて排ガス処
理し、得られた飛灰とセメントと水を14対1対11.
2の割合で混合し、この混合物を円筒型に流込んで固化
し、直径5cm、高さ10cmの円柱体のテストピース
を作製して20℃の室内で10日間養生し、これを東京
衝機製造所の圧縮機で圧縮試験することにより測定し
た。
<Comparative Test 2> The exhaust gas treating agents obtained in Examples 18 to 31 and Comparative Examples 7 to 9 were tested for the average particle size,
The whiteness, angle of repose, specific surface area, slurry viscosity, cement solidification strength and pressure loss were measured. Table 2 shows the results. The average particle size, whiteness, angle of repose, specific surface area, and pressure loss were measured in the same manner as in Comparative Test 1 described above. The slurry viscosity was obtained by mixing the obtained exhaust gas treating agent with water to prepare a slurry having a concentration of 30%, and measuring the viscosity of the slurry with a B-type viscometer. The smaller the value, the lower the viscosity. The cement solidification strength was determined by treating the exhaust gas using the obtained exhaust gas treating agent and treating the obtained fly ash, cement and water in a ratio of 14: 1 to 11: 1.
The mixture was poured into a cylinder and solidified to form a cylindrical test piece having a diameter of 5 cm and a height of 10 cm, and cured in a room at 20 ° C. for 10 days. It was measured by performing a compression test with a compressor at a place.

【0045】[0045]

【表2】 [Table 2]

【0046】表2から明らかな通り、実施例18〜31
で得られた排ガス処理剤は、白色度が高く、比表面積が
大きく、しかもスラリー粘性及び圧力損失が低かった。
一方、消化水にヘキシットを添加していない比較例7〜
9で得られた排ガス処理剤は、いずれも白色度が低く、
比表面積が小さく、スラリー粘性が高かった。比較例8
〜10のエタノールを添加した排ガス処理剤は、実施例
18〜31と比べて、安息角はほぼ同等であり、実施例
とともに流動性に優れていた。その反面、セメント固化
強度は実施例18〜31と比べて著しく劣っていた。
As is clear from Table 2, Examples 18 to 31
The exhaust gas treating agent obtained in (1) had high whiteness, a large specific surface area, and low slurry viscosity and low pressure loss.
On the other hand, Comparative Examples 7 to 7 in which hexit was not added to digested water
The exhaust gas treating agents obtained in 9 all have low whiteness,
The specific surface area was small and the slurry viscosity was high. Comparative Example 8
The exhaust gas treating agent to which ethanol was added was approximately the same in angle of repose as in Examples 18 to 31, and was excellent in fluidity together with Examples. On the other hand, the cement solidification strength was remarkably inferior to those of Examples 18 to 31.

【0047】更に、実施例18〜31で得られた排ガス
処理剤は平均粒子径は大きく、比較例7〜10はいずれ
も小さかった。特にエタノールを添加した排ガス処理剤
は添加量が多いほど小さいことが分かった。
Further, the exhaust gas treating agents obtained in Examples 18 to 31 had a large average particle diameter, and Comparative Examples 7 to 10 were all small. In particular, it was found that the larger the amount of the exhaust gas treating agent to which ethanol was added, the smaller the amount.

【0048】<平均粒径と圧力損失の比較>平均粒径と
圧力損失との関係を明確にするために、上記実施例1〜
31及び比較例1〜10の中から、平均粒径の異なるも
のを選び、それに対応する圧力損失を表3及び図1に示
す。
<Comparison between average particle size and pressure loss> In order to clarify the relationship between the average particle size and the pressure loss, the above Examples 1 to
31 and those having different average particle sizes are selected from Comparative Examples 1 to 10, and the corresponding pressure loss is shown in Table 3 and FIG.

【0049】[0049]

【表3】 [Table 3]

【0050】表3及び図1から明らかな通り、平均粒径
が7〜20μmの実施例10、28、30、31は、平
均粒径が6μm以下の比較例10、9、8、4、1と比
べて圧力損失が比較的小さいことが分った。
As is clear from Table 3 and FIG. 1, Examples 10, 28, 30, and 31 having an average particle diameter of 7 to 20 μm are Comparative Examples 10, 9, 8, 4, and 1 having an average particle diameter of 6 μm or less. It was found that the pressure loss was relatively small as compared with.

【0051】[0051]

【発明の効果】以上述べたように、本発明の排ガス処理
剤によれば、著しく比表面積が大きく反応性が高く、排
ガス中の有害な酸化物等を高効率で除去することがで
き、白色度が高いため製品の見栄えが良くその価値が高
まる。また粉体の製品になったときの流動性が良好であ
って、また排ガス処理時のスラリー状態の粘性が低いた
め、それぞれ配管への付着や閉塞を生じることがない。
また高温貯蔵でアルデヒドに変成する低級アルコールを
含んでいないため、保管貯蔵時に異臭を生じず、しかも
防爆設備を不要とし、火気に対して厳重な管理を必要と
せず、排ガス処理後のセメント固化したときの強度が高
く処分し易い利点がある。更に排ガス処理後のバグフィ
ルタの濾布の目詰りが生じにくく、その圧力損失を小さ
くすることができる。
As described above, according to the exhaust gas treating agent of the present invention, the specific surface area is remarkably large and the reactivity is high, and harmful oxides and the like in the exhaust gas can be removed with high efficiency. The higher the degree, the better the appearance of the product and its value. In addition, since the fluidity of the powdered product is good and the viscosity of the slurry during exhaust gas treatment is low, it does not adhere to the pipes or blockage.
In addition, because it does not contain lower alcohols that are converted to aldehydes during high-temperature storage, it does not generate off-flavors during storage and storage, does not require explosion-proof equipment, does not require strict control over fire, and has solidified cement after exhaust gas treatment. There is an advantage that the strength at the time is high and it is easy to dispose. Further, clogging of the filter cloth of the bag filter after the exhaust gas treatment hardly occurs, and the pressure loss can be reduced.

【図面の簡単な説明】[Brief description of the drawings]

【図1】実施例と比較例による平均粒径と圧力損失の関
係を示す図。
FIG. 1 is a diagram showing a relationship between an average particle diameter and a pressure loss according to an example and a comparative example.

【手続補正書】[Procedure amendment]

【提出日】平成9年12月5日[Submission date] December 5, 1997

【手続補正1】[Procedure amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0045[Correction target item name] 0045

【補正方法】変更[Correction method] Change

【補正内容】[Correction contents]

【0045】[0045]

【表2】 [Table 2]

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 水酸化カルシウムを主要成分とし、前記
水酸化カルシウムに対してヘキシットを0.1〜10重
量%含有し、比表面積が40m2/g以上であり、平均
粒径が7〜15μmである排ガス処理剤。
1. A composition comprising calcium hydroxide as a main component, 0.1 to 10% by weight of hexite based on calcium hydroxide, a specific surface area of 40 m 2 / g or more, and an average particle size of 7 to 15 μm. An exhaust gas treating agent.
【請求項2】 無機系鉱物、活性炭類及び軽量気泡コン
クリート廃材からなる群より選ばれた1種又は2種以上
の粉末を水酸化カルシウムに対して1〜50重量%均一
に混合した請求項1記載の排ガス処理剤。
2. The method of claim 1, wherein one or more powders selected from the group consisting of inorganic minerals, activated carbons and lightweight lightweight concrete concrete are uniformly mixed in an amount of 1 to 50% by weight with respect to calcium hydroxide. The exhaust gas treating agent according to the above.
【請求項3】 酸化カルシウムと水とを混合して前記酸
化カルシウムを消化させることにより水酸化カルシウム
を製造する方法において、ヘキシットを前記酸化カルシ
ウムに対して0.1〜10重量%の割合で前記酸化カル
シウムと混合することを特徴とする排ガス処理剤の製造
方法。
3. A method for producing calcium hydroxide by mixing calcium oxide and water to digest the calcium oxide, wherein hexit is added in a ratio of 0.1 to 10% by weight based on the calcium oxide. A method for producing an exhaust gas treating agent comprising mixing with an oxide of calcium.
【請求項4】 消化時の雰囲気を減圧する請求項3記載
の製造方法。
4. The method according to claim 3, wherein the atmosphere during digestion is reduced in pressure.
【請求項5】 消化のための水を2回に分けて酸化カル
シウムと混合し、1回目に混合する水にヘキシットを添
加し、2回目に添加する水にアルカリ水酸化物を添加す
る請求項3又は4記載の製造方法。
5. The method according to claim 1, wherein the water for digestion is divided into two portions and mixed with calcium oxide, hexit is added to the first mixed water, and alkali hydroxide is added to the second added water. 5. The production method according to 3 or 4.
【請求項6】 消化のための水量を酸化カルシウムの消
化当量の2〜5倍とし、生成した水分を含む水酸化カル
シウムを乾燥させる請求項3ないし5いずれか記載の製
造方法。
6. The method according to claim 3, wherein the amount of water for digestion is 2 to 5 times the digestion equivalent of calcium oxide, and the produced calcium hydroxide containing water is dried.
【請求項7】 ヘキシット水溶液に水より沸点の高い有
機溶剤をヘキシットに対して5〜100重量%の割合で
添加する請求項3ないし6いずれか記載の製造方法。
7. The method according to claim 3, wherein an organic solvent having a higher boiling point than water is added to the aqueous solution of Hexit at a ratio of 5 to 100% by weight based on Hexit.
【請求項8】 消化して生成された水酸化カルシウムに
無機系鉱物、活性炭類及び軽量気泡コンクリート廃材か
らなる群より選ばれた1種又は2種以上の粉末を添加混
合する請求項3ないし7いずれか記載の製造方法。
8. A method according to claim 3, wherein one or more powders selected from the group consisting of inorganic minerals, activated carbons and lightweight lightweight concrete concrete are added to the calcium hydroxide produced by digestion and mixed. The production method according to any of the above.
JP27572197A 1996-12-24 1997-10-08 Method for producing exhaust gas treating agent Expired - Lifetime JP3273907B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27572197A JP3273907B2 (en) 1996-12-24 1997-10-08 Method for producing exhaust gas treating agent

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP8-343370 1996-12-24
JP34337096 1996-12-24
JP27572197A JP3273907B2 (en) 1996-12-24 1997-10-08 Method for producing exhaust gas treating agent

Publications (2)

Publication Number Publication Date
JPH10249148A true JPH10249148A (en) 1998-09-22
JP3273907B2 JP3273907B2 (en) 2002-04-15

Family

ID=26551589

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Country Status (1)

Country Link
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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002210360A (en) * 2001-01-18 2002-07-30 Yoshizawa Lime Industry Treating agent for waste gas and treating method for the same
JP2006169062A (en) * 2004-12-17 2006-06-29 Ube Material Industries Ltd Porous particulate containing calcium oxide
JP2008212923A (en) * 2007-02-07 2008-09-18 Ryoko Lime Industry Co Ltd Exhaust gas treatment agent, and exhaust gas treating method and treatment system
JP2008290940A (en) * 2004-05-14 2008-12-04 Ube Material Industries Ltd Porous slaked lime
JP2008546631A (en) * 2005-06-28 2008-12-25 ソシエテ アノニム ロワ ルシェルシュ エ ディベロプマン Powdered lime composition, production process thereof and use thereof
JP4691770B2 (en) * 2000-10-06 2011-06-01 吉澤石灰工業株式会社 Method for producing highly reactive calcium hydroxide
JP2011116573A (en) * 2009-12-01 2011-06-16 Kotegawa Sangyo Kk Slaked lime, method for producing the same, and acidic gas removing agent
JP2013166676A (en) * 2012-02-16 2013-08-29 Kotegawa Sangyo Kk Slaked lime, method for producing slaked lime and acid gas removing agent
CN103408051A (en) * 2013-08-07 2013-11-27 中国科学院过程工程研究所 High-activity and high-strength coupled regulation and control method for agglomerated calcium oxide
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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4691770B2 (en) * 2000-10-06 2011-06-01 吉澤石灰工業株式会社 Method for producing highly reactive calcium hydroxide
JP2002210360A (en) * 2001-01-18 2002-07-30 Yoshizawa Lime Industry Treating agent for waste gas and treating method for the same
JP2008290940A (en) * 2004-05-14 2008-12-04 Ube Material Industries Ltd Porous slaked lime
JP2006169062A (en) * 2004-12-17 2006-06-29 Ube Material Industries Ltd Porous particulate containing calcium oxide
JP2008546631A (en) * 2005-06-28 2008-12-25 ソシエテ アノニム ロワ ルシェルシュ エ ディベロプマン Powdered lime composition, production process thereof and use thereof
JP2008212923A (en) * 2007-02-07 2008-09-18 Ryoko Lime Industry Co Ltd Exhaust gas treatment agent, and exhaust gas treating method and treatment system
JP2011116573A (en) * 2009-12-01 2011-06-16 Kotegawa Sangyo Kk Slaked lime, method for producing the same, and acidic gas removing agent
JP2013166676A (en) * 2012-02-16 2013-08-29 Kotegawa Sangyo Kk Slaked lime, method for producing slaked lime and acid gas removing agent
CN103408051A (en) * 2013-08-07 2013-11-27 中国科学院过程工程研究所 High-activity and high-strength coupled regulation and control method for agglomerated calcium oxide
KR102258357B1 (en) * 2021-04-01 2021-05-28 창녕군시설관리공단 Liquid slaked lime supply pump and pipe cleaning device for incineration facilities

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