JP2641401B2 - Activation method of slaked lime flue gas treatment agent - Google Patents

Activation method of slaked lime flue gas treatment agent

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Publication number
JP2641401B2
JP2641401B2 JP6311475A JP31147594A JP2641401B2 JP 2641401 B2 JP2641401 B2 JP 2641401B2 JP 6311475 A JP6311475 A JP 6311475A JP 31147594 A JP31147594 A JP 31147594A JP 2641401 B2 JP2641401 B2 JP 2641401B2
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JP
Japan
Prior art keywords
calcium
calcium hydroxide
flue gas
mixture
weight
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.)
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JP6311475A
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Japanese (ja)
Other versions
JPH08168636A (en
Inventor
朋弘 石塚
務 上野
岳史 村山
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.)
HOTSUKAIDO DENRYOKU KK
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HOTSUKAIDO DENRYOKU KK
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Description

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

【0001】[0001]

【産業上の利用分野】この発明は、従来、脱硫・脱硝性
能が低いとされていた水酸化カルシウムによる乾式排煙
処理の高活性化に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to high activation of dry flue gas treatment using calcium hydroxide, which was conventionally considered to have low desulfurization and denitration performance.

【0002】[0002]

【従来の技術】石炭、重油等の燃焼に伴い発生する排煙
中に含まれる硫黄酸化物、窒素酸化物等は、建物、構築
物等に害を与えるばかりではなく、動植物さらには人体
にも極めて大きな影響を及ぼすことが判明し、排煙中の
上記物質を除去する方法、すなわち脱硫、脱硝法が研究
され、多種多様な方式が開発されている。脱硫法は、大
きく分類して乾式、半乾式および湿式法に大別される。
本発明の属する乾式、半乾式には、表1に示す方法が知
られている。
2. Description of the Related Art Sulfur oxides, nitrogen oxides and the like contained in flue gas generated by the combustion of coal, heavy oil and the like not only harm buildings and structures, but also extremely affect animals, plants and the human body. It has been found that it has a great effect, and methods for removing the above substances in flue gas, that is, desulfurization and denitration methods have been studied, and various methods have been developed. Desulfurization methods are roughly classified into dry, semi-dry and wet methods.
The methods shown in Table 1 are known for the dry and semi-dry processes to which the present invention belongs.

【0003】[0003]

【表1】 表1に示した吸収法では、反応物質の再生(硫黄または
硫黄化合物の回収)のために高価なNH3 を必要とした
り(活性酸化マンガン法)、貴重な還元ガスを必要とし
たり(アルカライズドアルミナ法)、または反応温度が
高い(アルカライズドアルミナ法、石灰吹き込み法)と
いった問題点がある。吸着法では、使用する活性炭が高
価なこと、劣化しやすいといった欠点があり、接触酸化
法では、使用するバナジウム系触媒が高価な上、劣化し
やすく反応温度も比較的高いなどの問題点がある。
[Table 1] In the absorption method shown in Table 1, expensive NH 3 is required for the regeneration of the reactants (recovery of sulfur or a sulfur compound) (active manganese oxide method), or a valuable reducing gas is required (alcalizing). (Alumina method), or the reaction temperature is high (alkaline alumina method, lime blowing method). The adsorption method has the drawback that the activated carbon used is expensive and easily deteriorates.The catalytic oxidation method has the problems that the vanadium-based catalyst used is expensive and easily deteriorates, and the reaction temperature is relatively high. .

【0004】これまで水酸化カルシウムは高価であるに
もかかわらず反応効率が低いため、特に乾式法において
は積極的に利用されていなかった。このため、水酸化カ
ルシウムの活性をより高めるための種々の技術が研究さ
れている。その一つに消石灰に塩化カルシウムを添加す
る方式が提案されている(特開平3−161021)。
しかし、塩化カルシウムのみを水酸化カルシウムに添加
した場合、脱硫活性の向上は全く見られない。
Heretofore, calcium hydroxide has not been actively used, particularly in the dry process, because of its low reaction efficiency despite its high cost. For this reason, various techniques for further increasing the activity of calcium hydroxide have been studied. As one of them, a method of adding calcium chloride to slaked lime has been proposed (JP-A-3-161102).
However, when only calcium chloride is added to calcium hydroxide, no improvement in desulfurization activity is observed.

【0005】[0005]

【発明が解決しようとする課題】この発明の目的は、水
酸化カルシウムの脱硫活性を向上させることによって、
従来の乾式脱硫法の種々の問題点を解決し、廉価で高性
能の排煙処理剤を提供することおよびその排煙処理剤を
用いた排煙処理方法を提供することにある。
An object of the present invention is to improve the desulfurization activity of calcium hydroxide,
It is an object of the present invention to solve various problems of the conventional dry desulfurization method, to provide an inexpensive and high-performance flue gas treating agent, and to provide a flue gas treating method using the flue gas treating agent.

【0006】[0006]

【課題を解決するための手段】上記目的を達成するため
種々検討の結果、以下に説明するように、消石灰に塩化
カルシウムを添加した系にさらに炭酸カルシウムを存在
させることにより、著しく活性が向上することを見出し
た。また、スラリー状態で上記3成分を混合、乾燥して
得られた排煙処理剤は、理論的には不明な点が多いが、
全く脱硫活性の向上は見られないが、これに、さらに少
量の粉状の水酸化カルシウムを添加することで脱硫活性
が向上することを見出した。
As a result of various studies to achieve the above object, as described below, the activity is remarkably improved by further adding calcium carbonate to a system in which calcium chloride is added to slaked lime. I found that. The flue gas treating agent obtained by mixing and drying the above three components in a slurry state has many theoretically unknown points,
No improvement in the desulfurization activity was observed, but it was found that the desulfurization activity was improved by further adding a small amount of powdered calcium hydroxide.

【0007】すなわち、本発明は 1.水酸化カルシウムに粉状の塩化カルシウムを乾燥混
合物基準で1〜20重量%および粉状の炭酸カルシウム
を0.1〜20重量%になるよう添加し、そのまま、ま
たは乾燥することを特徴とする水酸化カルシウムを反応
物質とする粉状または粒子状の排煙処理剤の活性化方法 2.水酸化カルシウムを反応物質とする排煙処理剤の活
性化方法であって、水酸化カルシウム、塩化カルシウム
および炭酸カルシウムのスラリー混合物を調製し、乾燥
した後粉状の水酸化カルシウムをさらに加えて混合し、
得られた水酸化カルシウム、塩化カルシウムおよび炭酸
カルシウムの混合物基準で、混合物中の塩化カルシウム
が1〜20重量%、炭酸カルシウムが0.1〜20重量
%、残余を水酸化カルシウムとし、このうち後に加えた
粉状の水酸化カルシウムが、前記混合物基準で10〜5
0重量%になるよう調整することを特徴とする前記活性
化方法 3 水酸化カルシウムに粉状の塩化カルシウムを乾燥混
合物基準で1〜20重量%および粉状の炭酸カルシウム
を0.1〜20重量%になるよう添加し、そのまま、ま
たは乾燥して得られる水酸化カルシウムを反応物質とす
る粉状または粒子状の排煙処理剤を用い、60℃〜20
0℃の温度で排煙を処理することを特徴とする排煙処理
方法。および 4 水酸化カルシウム、塩化カルシウムおよび炭酸カル
シウムのスラリー混合物を調製し、乾燥した後粉状の水
酸化カルシウムをさらに加えて混合し、得られた水酸化
カルシウム、塩化カルシウムおよび炭酸カルシウムの混
合物基準で、混合物中の塩化カルシウムが1〜20重量
%、炭酸カルシウムが0.1〜20重量%、残余を水酸
化カルシウムとし、このうち後に加えた粉状の水酸化カ
ルシウムが、前記混合物基準で10〜50重量%になる
よう調整して得られる水酸化カルシウムを反応物質とす
る粉状または粒子状の排煙処理剤を用い、60℃〜20
0℃の温度で排煙を処理することを特徴とする排煙処理
方法である。
That is, the present invention provides: Water characterized by adding 1 to 20% by weight of powdered calcium chloride to calcium hydroxide and 0.1 to 20% by weight of powdered calcium carbonate on a dry mixture basis, and drying as it is or as water 1. A method for activating a powdery or particulate flue gas treating agent using calcium oxide as a reactant. A method for activating a flue gas treating agent using calcium hydroxide as a reactant, comprising preparing a slurry mixture of calcium hydroxide, calcium chloride and calcium carbonate, drying and then adding powdered calcium hydroxide to the mixture. And
Based on the obtained mixture of calcium hydroxide, calcium chloride and calcium carbonate, calcium chloride in the mixture is 1 to 20% by weight, calcium carbonate is 0.1 to 20% by weight, and the remainder is calcium hydroxide. The added powdery calcium hydroxide is 10 to 5 based on the mixture.
Said activation method characterized in that the content is adjusted to 0% by weight. 3-20% by weight of powdered calcium chloride and 0.1-20% by weight of powdered calcium carbonate based on a dry mixture of calcium hydroxide and calcium hydroxide. %, And using a powdery or particulate flue gas treating agent having calcium hydroxide obtained as it is or dried as a reactant, at 60 ° C to 20 ° C.
A method for treating flue gas, comprising treating flue gas at a temperature of 0 ° C. And 4 preparing a slurry mixture of calcium hydroxide, calcium chloride and calcium carbonate, drying and further adding powdered calcium hydroxide and mixing, based on the obtained mixture of calcium hydroxide, calcium chloride and calcium carbonate. The calcium chloride in the mixture is 1 to 20% by weight, the calcium carbonate is 0.1 to 20% by weight, and the balance is calcium hydroxide. The powdery calcium hydroxide added later is 10 to 10% by weight based on the mixture. Using a powdery or particulate flue gas treating agent containing calcium hydroxide as a reactant obtained by adjusting to 50% by weight, the temperature is from 60 ° C to 20 ° C.
This is a method for treating flue gas, wherein the flue gas is treated at a temperature of 0 ° C.

【0008】この発明で使用する水酸化カルシウム,塩
化カルシウム,炭酸カルシウムの純度等については特に
制限はなく、通常市場で入手できるものであれば、いず
れも使用できる。また純度が高ければ、副生品であって
もさしつかえない。
The purity of calcium hydroxide, calcium chloride and calcium carbonate used in the present invention is not particularly limited, and any one can be used as long as it is generally available on the market. If the purity is high, even by-products can be accepted.

【0009】添加すべき塩化カルシウムおよび炭酸カル
シウムの量は、添加後の乾燥混合物基準で塩化カルシウ
ムが1〜20重量%、炭酸カルシウムが0.1〜20重
量%、残りが水酸化カルシウムである。この範囲をはず
れると活性化の効果は損われる。
The amounts of calcium chloride and calcium carbonate to be added are 1 to 20% by weight of calcium chloride, 0.1 to 20% by weight of calcium carbonate, and the balance is calcium hydroxide, based on the dry mixture after addition. Outside this range, the effect of the activation will be impaired.

【0010】添加方法については、固体状で混合するこ
ともできるが、水酸化カルシウム、塩化カルシウム、炭
酸カルシウムの少なくとも一つのスラリーに、残りの材
料の粉体またはスラリーを加え、水酸化カルシウム、塩
化カルシウムおよび炭酸カルシウムを含むスラリー状混
合物を作り、乾燥した後さらに粉状の水酸化カルシウム
を加えることが好ましい。この場合の、仕上りの乾燥混
合物基準での塩化カルシウムおよび炭酸カルシウムの重
量割合は上記と同じ(それぞれ1〜20重量%および
0.1〜20重量%)であり、最後に加える粉状の水酸
化カルシウムの重量割合が仕上りの乾燥混合物基準で1
0〜50重量%になるように調整すればよい。添加、乾
燥、混合には公知のいずれの装置でも使用することがで
きる。
As to the method of addition, it is possible to mix in a solid state, but the powder or slurry of the remaining material is added to at least one slurry of calcium hydroxide, calcium chloride and calcium carbonate, and calcium hydroxide, chloride It is preferable to prepare a slurry-like mixture containing calcium and calcium carbonate, and after drying, further add powdered calcium hydroxide. In this case, the weight ratio of calcium chloride and calcium carbonate based on the finished dry mixture is the same as above (1 to 20% by weight and 0.1 to 20% by weight, respectively), The weight ratio of calcium is 1 based on the finished dry mixture.
What is necessary is just to adjust so that it may become 0 to 50 weight%. Any known apparatus can be used for addition, drying, and mixing.

【0011】上記の添加方法により得られた混合物は粉
状または粒状で排煙処理剤として使用することができ
る。粉状で用いる場合は、煙道噴霧、流動層あるいは噴
流層などの方法で使用することができる。粒状で用いる
場合は、粉状のものをディスクペレッター等の公知の方
法によって成形し移動層、固定層、流動層、噴流層にお
いて使用することができる。適用できる排煙としては、
石炭、石油燃焼ボイラの排煙のほか、HCl等の酸性ガ
スを含む排煙、具体的にはごみ焼却ボイラ等の排煙も処
理することができる。排煙の処理温度は室温〜300
℃、好ましくは60〜200℃である。
The mixture obtained by the above-mentioned addition method can be used as a flue gas treating agent in powder or granular form. When used in powder form, it can be used by methods such as flue spray, fluidized bed or spouted bed. When used in a granular form, a powdery substance can be formed by a known method such as a disk pelletizer and used in a moving bed, a fixed bed, a fluidized bed, and a spouted bed. Applicable smoke emissions include:
In addition to flue gas from coal and oil-fired boilers, it can also treat flue gas containing acidic gas such as HCl, and more specifically, flue gas from refuse incineration boilers and the like. Exhaust gas treatment temperature is from room temperature to 300
° C, preferably 60 to 200 ° C.

【0012】[0012]

【実施例】【Example】

実施例1 市販の水酸化カルシウムに所定量の市販の炭酸カルシウ
ム、および市販の粒子状無水塩化カルシウムを粉状にし
て混合し、水酸化カルシウムを活性化した。表2に示し
た試験条件で性能評価試験を行い、脱硫率が80%を破
過するまでに要した時間を吸収剤に含まれるCa(O
H)2中のCa当量に換算した値を表3に示した。
Example 1 A predetermined amount of commercially available calcium carbonate and commercially available particulate anhydrous calcium chloride were powdered and mixed with commercially available calcium hydroxide to activate the calcium hydroxide. A performance evaluation test was performed under the test conditions shown in Table 2, and the time required for the desulfurization rate to exceed 80% was determined by the amount of Ca (O
Table 3 shows the values converted to Ca equivalents in H) 2 .

【0013】なお、同表に比表面積の測定結果も併記し
た。比表面積の測定は、試料を300℃で1時間脱ガス
した後BET法で行った。
The results of the measurement of the specific surface area are also shown in the table. The specific surface area was measured by a BET method after degassing the sample at 300 ° C. for 1 hour.

【0014】実施例2 市販の無水塩化カルシウムの所定量を95℃の水溶液と
し、これに市販の水酸化カルシウムおよび炭酸カルシウ
ムを表3に示した割合で添加してスラリー濃度を16.
7%とし、30分攪拌した後、200℃で2時間乾燥さ
せ、さらに粉状の水酸化カルシウムを混合して活性化し
た排煙処理剤を得た。実施例1と同様の性能評価試験を
行い、結果を表3に示した。
Example 2 A predetermined amount of commercially available anhydrous calcium chloride was used as an aqueous solution at 95 ° C., and commercially available calcium hydroxide and calcium carbonate were added thereto in the proportions shown in Table 3 to reduce the slurry concentration to 16.
After stirring for 30 minutes, the mixture was dried at 200 ° C. for 2 hours, and powdered calcium hydroxide was mixed to obtain an activated flue gas treating agent. The same performance evaluation test as in Example 1 was performed, and the results are shown in Table 3.

【0015】実施例3 粉状の工業用消石灰(CaCO3 含有量7%)に所定量
の市販の粒子状無水塩化カルシウムを粉状にし混合して
活性化した排煙処理剤を得た。実施例1と同様の性能評
価試験を行い、結果を表3に示した。
Example 3 A predetermined amount of commercially available anhydrous calcium chloride was powdered and mixed with powdered industrial slaked lime (CaCO 3 content: 7%) to obtain an activated flue gas treating agent. The same performance evaluation test as in Example 1 was performed, and the results are shown in Table 3.

【0016】実施例4 市販の炭酸カルシウムと石炭の混合物(混合比8:2)
を900℃で焼成した後、スラリー濃度16.7%とな
るように65℃の水で水和反応を行った。これを200
℃で2時間乾燥し、所定量の市販の粒子状無水塩化カル
シウムを粉状にし混合して活性化した排煙処理剤を得
た。実施例1と同様の性能評価試験を行い、結果を表3
に示した。
Example 4 Commercially available mixture of calcium carbonate and coal (mixing ratio 8: 2)
Was calcined at 900 ° C., and a hydration reaction was performed with water at 65 ° C. so that the slurry concentration was 16.7%. This is 200
After drying at 2 ° C. for 2 hours, a predetermined amount of commercially available particulate anhydrous calcium chloride was powdered and mixed to obtain an activated flue gas treating agent. The same performance evaluation test as in Example 1 was performed, and the results were shown in Table 3.
It was shown to.

【0017】実施例5 半乾式法で使用した使用済消石灰吸収剤(表4に組成を
表記)を消化反応が終った直後の95℃の消石灰スラリ
ーに所定量を添加し、200℃で2時間乾燥後、所定量
の市販の粒子状無水塩化カルシウムを粉状にし混合して
活性化した排煙処理剤を得た。実施例1と同様の性能試
験を行い、結果を表3に示した。
Example 5 A predetermined amount of a used slaked lime absorbent (the composition is shown in Table 4) used in the semi-dry method was added to a slaked lime slurry at 95 ° C immediately after the digestion reaction was completed, and the mixture was added at 200 ° C for 2 hours After drying, a predetermined amount of commercially available particulate anhydrous calcium chloride was powdered and mixed to obtain an activated flue gas treating agent. The same performance test as in Example 1 was performed, and the results are shown in Table 3.

【0018】比較例1 市販の水酸化カルシウムについて実施例1と同様の性能
評価試験を行い、結果を表3に示した。
Comparative Example 1 A commercially available calcium hydroxide was subjected to the same performance evaluation test as in Example 1, and the results are shown in Table 3.

【0019】比較例2 市販の無水塩化カルシウムについて性能評価試験を行
い、結果を表3に示した。
Comparative Example 2 A performance evaluation test was performed on commercially available anhydrous calcium chloride, and the results are shown in Table 3.

【0020】比較例3 市販の炭酸カルシウムについて性能評価試験を行い、結
果を表3に示した。
Comparative Example 3 A performance evaluation test was performed on commercially available calcium carbonate, and the results are shown in Table 3.

【0021】比較例4 粉状の工業用消石灰(CaCO3 含有7%)について実
施例1と同様の性能評価試験を行い、結果を表3に示し
た。
Comparative Example 4 A powdery industrial hydrated lime (CaCO 3 content: 7%) was subjected to the same performance evaluation test as in Example 1, and the results are shown in Table 3.

【0022】比較例5 市販の水酸化カルシウムに、所定量の市販の粒子状無水
塩化カルシウムを粉状にして混合した。実施例1と同様
の性能評価試験を行い、結果を表3に示した。 比較例6 市販の無水塩化カルシウムの所定量を95℃の水溶液と
し、これに市販の水酸化カルシウムおよび炭酸カルシウ
ムを表3に示した割合で添加してスラリー濃度を16.
7%とし、30分攪拌した後、200℃で2時間乾燥さ
せて排煙処理剤を得た。実施例1と同様の性能評価試験
を行い、結果を表3に示した。
Comparative Example 5 A commercially available calcium hydroxide was mixed with a predetermined amount of commercially available particulate anhydrous calcium chloride in powder form. The same performance evaluation test as in Example 1 was performed, and the results are shown in Table 3. Comparative Example 6 A predetermined amount of commercially available anhydrous calcium chloride was used as an aqueous solution at 95 ° C., and commercially available calcium hydroxide and calcium carbonate were added thereto in the proportions shown in Table 3 to reduce the slurry concentration to 16.
After stirring for 30 minutes, the mixture was dried at 200 ° C. for 2 hours to obtain a smoke emission treating agent. The same performance evaluation test as in Example 1 was performed, and the results are shown in Table 3.

【0023】[0023]

【表2】 [Table 2]

【0024】[0024]

【表3】 [Table 3]

【0025】[0025]

【表4】 [Table 4]

【0026】[0026]

【発明の効果】この発明によれば、消石灰の排煙処理剤
としての活性を向上させることができ、乾式、または半
乾式において比較的廉価な高活性排煙処理剤を提供する
ことが可能になった。
According to the present invention, the activity of slaked lime as a flue gas treatment agent can be improved, and a dry or semi-dry type, relatively inexpensive, highly active flue gas treatment agent can be provided. became.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 村山 岳史 北海道札幌市豊平区美しが丘4条9丁目 2番1号 北海道電力株式会社 総合研 究所内 (56)参考文献 特開 平5−57139(JP,A) ──────────────────────────────────────────────────続 き Continuation of the front page (72) Inventor Takeshi Murayama 4-1, 9-9, Migaoka, Toyohira-ku, Sapporo, Hokkaido Hokkaido Electric Power Company Research Institute (56) References JP-A-5-57139 (JP, A)

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 水酸化カルシウムに粉状の塩化カルシウ
ムを乾燥混合物基準で1〜20重量%および粉状の炭酸
カルシウムを0.1〜20重量%になるよう添加し、そ
のまま、または乾燥することを特徴とする水酸化カルシ
ウムを反応物質とする粉状または粒子状の排煙処理剤の
活性化方法。
1. A method in which powdered calcium chloride is added to calcium hydroxide in an amount of 1 to 20% by weight and dry powdered calcium carbonate in an amount of 0.1 to 20% by weight based on a dry mixture, and dried as it is or as it is. A method for activating a powdery or particulate flue gas treating agent comprising calcium hydroxide as a reactant.
【請求項2】 水酸化カルシウムを反応物質とする排煙
処理剤の活性化方法であって、水酸化カルシウム、塩化
カルシウムおよび炭酸カルシウムのスラリー混合物を調
製し、乾燥した後粉状の水酸化カルシウムをさらに加え
て混合し、得られた水酸化カルシウム、塩化カルシウム
および炭酸カルシウムの混合物基準で、混合物中の塩化
カルシウムが1〜20重量%、炭酸カルシウムが0.1
〜20重量%、残余を水酸化カルシウムとし、このうち
後に加えた粉状の水酸化カルシウムが、前記混合物基準
で10〜50重量%になるよう調整することを特徴とす
る前記活性化方法。
2. A method for activating a flue gas treating agent comprising calcium hydroxide as a reactant, comprising preparing a slurry mixture of calcium hydroxide, calcium chloride and calcium carbonate, drying the mixture, and then powdering calcium hydroxide. Are further added and mixed, and based on the obtained mixture of calcium hydroxide, calcium chloride and calcium carbonate, 1 to 20% by weight of calcium chloride and 0.1% of calcium carbonate are contained in the mixture.
-20% by weight, the balance being calcium hydroxide, wherein the powdery calcium hydroxide added later is adjusted to 10-50% by weight based on the mixture.
【請求項3】 水酸化カルシウムに粉状の塩化カルシウ
ムを乾燥混合物基準で1〜20重量%および粉状の炭酸
カルシウムを0.1〜20重量%になるよう添加し、そ
のまま、または乾燥して得られる水酸化カルシウムを反
応物質とする粉状または粒子状の排煙処理剤を用い、6
0℃〜200℃の温度で排煙を処理することを特徴とす
る排煙処理方法。
3. A powdered calcium chloride is added to calcium hydroxide in an amount of 1 to 20% by weight and a powdered calcium carbonate in an amount of 0.1 to 20% by weight based on a dry mixture, and the calcium hydroxide is dried as it is or as it is. Using a powdery or particulate flue gas treating agent containing the obtained calcium hydroxide as a reactant, 6
A method for treating flue gas, comprising treating flue gas at a temperature of 0 ° C to 200 ° C.
【請求項4】 水酸化カルシウム、塩化カルシウムおよ
び炭酸カルシウムのスラリー混合物を調製し、乾燥した
後粉状の水酸化カルシウムをさらに加えて混合し、得ら
れた水酸化カルシウム、塩化カルシウムおよび炭酸カル
シウムの混合物基準で、混合物中の塩化カルシウムが1
〜20重量%、炭酸カルシウムが0.1〜20重量%、
残余を水酸化カルシウムとし、このうち後に加えた粉状
の水酸化カルシウムが、前記混合物基準で10〜50重
量%になるよう調整して得られる水酸化カルシウムを反
応物質とする粉状または粒子状の排煙処理剤を用い、6
0℃〜200℃の温度で排煙を処理することを特徴とす
る排煙処理方法。
4. A slurry mixture of calcium hydroxide, calcium chloride and calcium carbonate is prepared, and after drying, powdery calcium hydroxide is further added and mixed, and the resulting calcium hydroxide, calcium chloride and calcium carbonate are mixed. 1 calcium chloride in the mixture, based on the mixture
-20% by weight, 0.1-20% by weight of calcium carbonate,
The remainder is calcium hydroxide, and powdery or particulate form containing calcium hydroxide obtained by adjusting the amount of powdered calcium hydroxide added later to be 10 to 50% by weight based on the mixture, as a reactant. Using a flue gas treatment agent
A method for treating flue gas, comprising treating flue gas at a temperature of 0 ° C to 200 ° C.
JP6311475A 1994-12-15 1994-12-15 Activation method of slaked lime flue gas treatment agent Expired - Lifetime JP2641401B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6311475A JP2641401B2 (en) 1994-12-15 1994-12-15 Activation method of slaked lime flue gas treatment agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6311475A JP2641401B2 (en) 1994-12-15 1994-12-15 Activation method of slaked lime flue gas treatment agent

Publications (2)

Publication Number Publication Date
JPH08168636A JPH08168636A (en) 1996-07-02
JP2641401B2 true JP2641401B2 (en) 1997-08-13

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Country Link
JP (1) JP2641401B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6031645B2 (en) * 2012-03-30 2016-11-24 国立研究開発法人 海上・港湾・航空技術研究所 Desulfurization agent, desulfurization method and method for producing desulfurization agent

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0557139A (en) * 1991-08-30 1993-03-09 Babcock Hitachi Kk Lime blowing desulfurization

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Publication number Publication date
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