JPH0253085B2 - - Google Patents

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Publication number
JPH0253085B2
JPH0253085B2 JP62131873A JP13187387A JPH0253085B2 JP H0253085 B2 JPH0253085 B2 JP H0253085B2 JP 62131873 A JP62131873 A JP 62131873A JP 13187387 A JP13187387 A JP 13187387A JP H0253085 B2 JPH0253085 B2 JP H0253085B2
Authority
JP
Japan
Prior art keywords
desulfurization
composition
exhaust gas
calcium
curing
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 - Lifetime
Application number
JP62131873A
Other languages
Japanese (ja)
Other versions
JPS63296827A (en
Inventor
Tsutomu Ueno
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.)
Hokkaido Electric Power Co Inc
Original Assignee
Hokkaido Electric Power Co Inc
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 Hokkaido Electric Power Co Inc filed Critical Hokkaido Electric Power Co Inc
Priority to JP62131873A priority Critical patent/JPS63296827A/en
Publication of JPS63296827A publication Critical patent/JPS63296827A/en
Publication of JPH0253085B2 publication Critical patent/JPH0253085B2/ja
Granted legal-status Critical Current

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  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

〔産業上の利用分野〕 本発明は、石炭、重油等の燃料の燃焼、都市ゴ
ミ等の廃棄物、その他の燃焼、乾燥、焙焼等に伴
う排ガスの脱硫方法に関する。 〔従来の技術〕 石炭、重油等の燃焼に伴い発生する排ガス中に
含まれる硫黄酸化物および窒素酸化物等は、建
物、構築物等に害を与えるばかりでなく、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、排ガス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。 これらの脱硫、脱硝法は乾式法および湿式法に
大別される。本発明の属する乾式脱硫法には第1
表に示す方法が示されている。
[Industrial Field of Application] The present invention relates to a method for desulfurizing exhaust gases accompanying the combustion of fuels such as coal and heavy oil, wastes such as municipal garbage, and other combustion, drying, and roasting. [Prior art] Sulfur oxides, nitrogen oxides, etc. contained in the exhaust gas generated from the combustion of coal, heavy oil, etc. not only harm buildings, structures, etc., but are also extremely harmful to animals, plants, and even the human body. It has been found that these substances have a significant impact, and methods for removing the above substances from exhaust gas, namely desulfurization and denitration methods, have been studied and a wide variety of methods have been developed. These desulfurization and denitrification methods are broadly classified into dry methods and wet methods. The dry desulfurization method to which the present invention belongs includes the first
The methods shown in the table are shown.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

本発明の目的は、上述の従来の乾式脱硫方式の
種々の問題点を解決し、低廉な原料から比較的簡
単な製法で得られる硬化組成物を使用した新規な
脱硫方法を提供することにある。 〔問題点を解決するための手段〕 本発明は、酸化カルシウムを供給できる物質と
硫酸化合物、ハロゲン元素化合物、二酸化ケイ
素、酸化アルミニウム、硫化物、アルカリ金属の
水酸化物を供給できる物質の群から選ばれた1種
以上の物質を原料としてなる硬化組成物による排
ガスの脱硫において窒素酸化物を排ガス中の亜硫
酸ガス1モル当り0.01モル以上添加することを特
徴とする排ガス脱硫方法である。 先ず本発明の方法に使用する硬化組成物の原料
について説明する。酸化カルシウムを供給できる
物質としては、例えば、生石灰、消石灰、炭酸石
灰、セメント、スラグ、ドロマイトプラスター
(石灰含有)およびアセチレン滓などの副生品等
があげられる。 硫酸化合物、ハロゲン元素化合物を供給できる
物質とは、例えば、カルシウム、マグネシウムな
どのアルカリ土類金属、ナトリウム、カリウム等
のアルカリ金属と硫酸、ハロゲン化水素とを組合
せることによつて生成する物質で硫酸カルシウ
ム、硫酸マグネシウム、塩化カルシウム、塩化マ
グネシウム、硫酸ナトリウム、硫酸カリウム、亜
硫酸カルシウム、硫酸水素カルシウム、塩化ナト
リウム、塩化ストロンチウム、臭化カルシウム、
ヨウ化カルシウム、塩化カリウム、チオ硫酸ナト
リウム、炭酸水素ナトリウム、炭酸水素カルシウ
ム、黒液燃焼灰等があげられる。 二酸化ケイ素を供給しうる物質としては、例え
ば、ケイ酸、含水ケイ酸、メタケイ酸、ケイ酸ア
ルミニウム、ケイ酸カルシウムおよびクリストバ
ライト、トリジマイト、カオリン、ベントナイ
ト、タルク、パーライト、シラス、ケイソウ土、
ガラス等反応性二酸化ケイ素を含有する化合物な
どがあげられる。酸化アルミニウムを供給しうる
物質としては、例えばアルミナ、水酸化アルミニ
ウム、ケイ酸アルミニウム、硫酸ばん土、明ば
ん、硫化アルミニウム、硫酸アルミニウム、塩化
アルミニウム、ベントナイト、カオリン、ケイソ
ウ土、ゼオライト、パーライト、アルミン酸ナト
リウム、氷晶石、ボーキサイト等反応性アルミニ
ウムを含有する化合物などがあげられる。 硫化物を供給できる物質としては、例えば硫化
カルシウム、硫化鉄、硫化亜鉛等があげられる。 アルカリ金属の水酸化物を供給できる物質とし
ては、水酸化ナトリウム、水酸化カリウム等があ
げられる。 また前述の6種の化合物中2種以上を同時に供
給しうる他の物質の例として、石炭灰および火山
灰、石炭流動層燃焼灰(酸化カルシウム、二酸化
ケイ素、酸化アルミニウム、硫酸カルシウム、硫
酸ナトリウム、硫酸カリウム源)、セメントおよ
びセメントクリンカー(酸化アルミニウム、硫酸
カルシウム、二酸化ケイ素、酸化アルミニウム
源)、スラグおよびシラス、安山岩 チヤート、
石英粗面岩、オパール、沸石、長石、粘土鉱物、
エトリンガイト(酸化ナトリウム、二酸化ケイ
素、酸化アルミニウム、酸化カルシウム)などの
反応性二酸化ケイ素、ナトリウム、アルミニウ
ム、カルシウム等および塩化物、硫酸塩等を含有
する鉱物、更に流動層燃焼灰等の炉内脱硫灰およ
び煙道脱硫後の廃脱硫剤、汚泥焼却灰、都市ゴミ
焼却灰、セメントくず、アセチレン滓等の廃棄物
があげられる。 更に、これまでに記述した所要材料が、例えば
単体イオウを添加することによつて材料間の相互
の反応が進行し、その結果、硫化カルシウム、硫
酸カルシウム等を生成して供給されるような場
合、さらにケイ酸と苛性アルカリが反応して生成
される水ガラスなどおよび硫酸、塩酸などを加え
て生成する物質も含まれる。第2表に原料の化学
組成の1例を示す。
The purpose of the present invention is to solve the various problems of the conventional dry desulfurization method described above, and to provide a new desulfurization method using a cured composition obtained by a relatively simple manufacturing method from inexpensive raw materials. . [Means for Solving the Problems] The present invention provides a method for using a substance that can supply calcium oxide and a substance that can supply sulfuric acid compounds, halogen element compounds, silicon dioxide, aluminum oxide, sulfides, and alkali metal hydroxides. This is an exhaust gas desulfurization method characterized in that 0.01 mol or more of nitrogen oxide is added per 1 mol of sulfur dioxide gas in the exhaust gas when desulfurizing the exhaust gas using a curing composition made of one or more selected substances as raw materials. First, the raw materials for the cured composition used in the method of the present invention will be explained. Examples of substances that can supply calcium oxide include by-products such as quicklime, slaked lime, carbonated lime, cement, slag, dolomite plaster (containing lime), and acetylene slag. Substances that can supply sulfuric compounds and halogen element compounds include, for example, substances produced by combining alkaline earth metals such as calcium and magnesium, alkali metals such as sodium and potassium, and sulfuric acid and hydrogen halides. Calcium sulfate, magnesium sulfate, calcium chloride, magnesium chloride, sodium sulfate, potassium sulfate, calcium sulfite, calcium hydrogen sulfate, sodium chloride, strontium chloride, calcium bromide,
Examples include calcium iodide, potassium chloride, sodium thiosulfate, sodium hydrogen carbonate, calcium hydrogen carbonate, and black liquor combustion ash. Substances that can supply silicon dioxide include, for example, silicic acid, hydrous silicic acid, metasilicic acid, aluminum silicate, calcium silicate, cristobalite, tridymite, kaolin, bentonite, talc, perlite, shirasu, diatomaceous earth,
Examples include compounds containing reactive silicon dioxide such as glass. Substances that can supply aluminum oxide include, for example, alumina, aluminum hydroxide, aluminum silicate, sulfuric acid, alum, aluminum sulfide, aluminum sulfate, aluminum chloride, bentonite, kaolin, diatomaceous earth, zeolite, pearlite, and aluminic acid. Examples include compounds containing reactive aluminum such as sodium, cryolite, and bauxite. Examples of substances that can supply sulfide include calcium sulfide, iron sulfide, and zinc sulfide. Examples of substances capable of supplying alkali metal hydroxides include sodium hydroxide and potassium hydroxide. Examples of other substances that can simultaneously supply two or more of the six compounds mentioned above include coal ash, volcanic ash, coal fluidized bed combustion ash (calcium oxide, silicon dioxide, aluminum oxide, calcium sulfate, sodium sulfate, sulfuric acid potassium source), cement and cement clinker (aluminum oxide, calcium sulfate, silicon dioxide, aluminum oxide source), slag and shirasu, andesite chaat,
quartz trachyte, opal, zeolite, feldspar, clay minerals,
Minerals containing reactive silicon dioxide such as ettringite (sodium oxide, silicon dioxide, aluminum oxide, calcium oxide), sodium, aluminum, calcium, etc., chlorides, sulfates, etc., as well as in-furnace desulfurization ash such as fluidized bed combustion ash. and wastes such as waste desulfurization agent after flue desulfurization, sludge incineration ash, municipal garbage incineration ash, cement waste, and acetylene slag. Furthermore, when the required materials described so far are supplied by adding elemental sulfur, for example, a mutual reaction between the materials progresses, resulting in the production of calcium sulfide, calcium sulfate, etc. It also includes water glass produced by the reaction of silicic acid and caustic alkali, and substances produced by adding sulfuric acid, hydrochloric acid, etc. Table 2 shows an example of the chemical composition of the raw materials.

【表】【table】

〔実施例〕〔Example〕

実施例 1 石炭灰77重量部、水酸化カルシウム15重量部、
2水石膏8重量部、(無水ベース)を混合し、水
40重量部を加えて混練後、100℃で24時間蒸気養
生し、破砕し粒径を0.5〜0.71mmに揃え、100℃で
1時間熱処理して本発明の脱硫剤を得た。ここに
使用した石炭灰の分析値は第3表のとおりであ
る。 脱硫試験は、第4表に示す試験条件(130℃、
SV10000h-1)で行つた。 脱硫率の算出は、通ガス後3時間の積分値とし
た。
Example 1 77 parts by weight of coal ash, 15 parts by weight of calcium hydroxide,
Mix 8 parts by weight of dihydrate gypsum (anhydrous base), add water
After adding 40 parts by weight and kneading, the mixture was steam-cured at 100°C for 24 hours, crushed to have a particle size of 0.5 to 0.71 mm, and heat-treated at 100°C for 1 hour to obtain the desulfurizing agent of the present invention. The analytical values of the coal ash used here are shown in Table 3. The desulfurization test was conducted under the test conditions shown in Table 4 (130℃,
I went with SV10000h -1 ). The desulfurization rate was calculated using the integral value for 3 hours after gas passage.

【表】【table】

【表】 上記基準ガスにNOxを第5表に示す濃度とな
るように添加して、脱硫率を測定し同表にまとめ
た。
[Table] NOx was added to the above reference gas at a concentration shown in Table 5, and the desulfurization rate was measured and summarized in the same table.

【表】 上記試験において添加したNOxは、上記濃度
範囲で77%以上除去される。したがつて処理後の
排ガス中に残留が許容されるNOxの濃度の範囲
内でNOx/SO2のモル比を適当にえらび、高い
脱硫率を得ることができる。しかも上表によれ
ば、NOx含有ガス通過後NOxをゼロにしても最
初からNOxを含まない場合の脱硫率より遥かに
高い値を示すが、これはNOxの脱硫剤に対する
残留効果の表われと思われる。 実施例 2〜12 市販の消石灰、硫酸カルシウム、ケイ酸、水酸
化アルミニウム、ケイ酸カルシウム、ケイ酸アル
ミニウムを第6表に示す配合に従つて混合し、水
を加えて再度混合し、常圧100℃の蒸気養生を24
時間行い、得られた硬化物を破砕して粒径0.5〜
0.7mmに整粒し、130℃で2時間熱処理して本発明
の脱硫方法に使用する脱硫剤を得た。該剤中の
CaO、CaSO4、SiO2、Al2O3換算重量100分率
(以下基材組成と記す)を性能試験結果と共に第
7表に示す。 性能試験は、第4表に示す試験条件でNOxを
100ppm添加した場合と、無添加の場合に脱硫試
験(SO2除去試験)を行い、第7表にその結果を
示した。なお同表に供試脱硫剤の比表面積の測定
値も並記した。比表面積の測定は、試料を200℃
で1時間脱ガスした後BET法で行つた。
[Table] More than 77% of the NOx added in the above test was removed within the above concentration range. Therefore, a high desulfurization rate can be obtained by appropriately selecting the NOx/SO 2 molar ratio within the range of NOx concentration that is allowed to remain in the exhaust gas after treatment. Moreover, according to the table above, even if NOx is reduced to zero after the NOx-containing gas has passed through, the desulfurization rate is much higher than the desulfurization rate when NOx is not included from the beginning, but this is an expression of the residual effect of NOx on the desulfurization agent. Seem. Examples 2 to 12 Commercially available slaked lime, calcium sulfate, silicic acid, aluminum hydroxide, calcium silicate, and aluminum silicate were mixed according to the formulation shown in Table 6, water was added and mixed again, and the mixture was heated at normal pressure 100 Steam curing at 24 °C
The resulting cured product is crushed to a particle size of 0.5~
The particles were sized to 0.7 mm and heat treated at 130° C. for 2 hours to obtain a desulfurization agent used in the desulfurization method of the present invention. in the agent
Table 7 shows CaO, CaSO 4 , SiO 2 , Al 2 O 3 equivalent weight percentage (hereinafter referred to as base material composition) along with the performance test results. The performance test was conducted under the test conditions shown in Table 4.
A desulfurization test (SO 2 removal test) was conducted with and without addition of 100 ppm, and the results are shown in Table 7. In addition, the measured values of the specific surface area of the test desulfurization agents are also listed in the same table. To measure the specific surface area, heat the sample to 200℃.
After degassing for 1 hour, the BET method was used.

【表】【table】

【表】 実施例 13 石炭灰、水酸化カルシウム、2水石膏を下表に
示す割合で用いた以外は実施例1と同様の操作で
本発明に使用する脱硫剤を得、NOxの添加量を
240ppmに固定し温度を30゜〜1000℃に変えた以外
は実施例1と同じ試験を行つて脱硫率を算出し
た。結果を第1図に示した。 これによると、この脱硫率の温度による影響は
反応温度30゜〜900℃でほとんど認められない。
[Table] Example 13 A desulfurizing agent used in the present invention was obtained in the same manner as in Example 1, except that coal ash, calcium hydroxide, and dihydrate gypsum were used in the proportions shown in the table below, and the amount of NOx added was
The desulfurization rate was calculated by conducting the same test as in Example 1, except that the temperature was fixed at 240 ppm and the temperature was changed from 30° to 1000°C. The results are shown in Figure 1. According to this, almost no influence of temperature on the desulfurization rate is observed at reaction temperatures of 30° to 900°C.

【表】 * 無水換算
〔発明の効果〕 以上詳細に述べたように、石灰系硬化組成物を
用いた脱硫において、処理ガス中にNOxを添加
することにより脱硫率を向上させることができる
と共に添加したNOxの濃度も低下する。したが
つて本発明の脱硫方法によれば脱硝すべき排ガス
のある場合、これを利用して脱硫と脱硝を同時に
効率よく行うことができ、工業的価値は大きい。
[Table] * Anhydrous equivalent [Effect of the invention] As described in detail above, in desulfurization using a lime-based curing composition, the desulfurization rate can be improved by adding NOx to the treated gas, and the addition The concentration of NOx also decreases. Therefore, according to the desulfurization method of the present invention, when there is exhaust gas to be denitrified, desulfurization and denitration can be efficiently carried out simultaneously using this gas, which has great industrial value.

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

第1図は本発明の方法における温度と脱硫率の
関係を表わす図である。
FIG. 1 is a diagram showing the relationship between temperature and desulfurization rate in the method of the present invention.

Claims (1)

【特許請求の範囲】 1 酸化カルシウムを供給できる物質と、硫酸化
合物、ハロゲン元素化合物、二酸化ケイ素、酸化
アルミニウム、硫化物およびアルカリ金属の水酸
化物を供給できる物質の群から選ばれた1種以上
の物質を原料としてなる硬化組成物による排ガス
の脱硫において、窒素酸化物を排ガス中の亜硫酸
ガス1モル当り0.01モル以上添加することを特徴
とする排ガスの脱硫方法。 2 硬化組成物が、原料を水と混合した後成形
し、あるいは湿空養生または蒸気養生した後成形
し、そのまままたは30℃以上の温度で熱処理した
ものである特許請求の範囲第1項記載の脱硫方
法。 3 硬化組成物が、原料を水と混合し、湿空養生
または蒸気養生した後成形し、再度湿空養生また
は蒸気養生を行い、そのまままたは30℃以上の温
度で熱処理したものである特許請求の範囲第1項
記載の脱硫方法。 4 窒素酸化物の濃度が間欠的に変化するように
添加する特許請求の範囲第1項記載の脱硫方法。
[Scope of Claims] 1. One or more substances selected from the group of substances capable of supplying calcium oxide and substances capable of supplying sulfuric compounds, halogen element compounds, silicon dioxide, aluminum oxide, sulfides, and alkali metal hydroxides. 1. A method for desulfurizing exhaust gas, which comprises adding 0.01 mol or more of nitrogen oxide per 1 mol of sulfur dioxide gas in the exhaust gas, in the desulfurization of exhaust gas using a hardening composition made from the substance described above. 2. The cured composition according to claim 1, wherein the cured composition is obtained by mixing raw materials with water and then molding, or by curing in a humid air or steam, and then molding, and then heat-treating the composition as it is or at a temperature of 30°C or higher. Desulfurization method. 3. A patent claim in which the cured composition is obtained by mixing raw materials with water, curing in humid air or steam, molding the composition, curing in humid air or steam again, and then heat-treating the composition as it is or at a temperature of 30°C or higher. The desulfurization method according to scope 1. 4. The desulfurization method according to claim 1, wherein nitrogen oxides are added so that the concentration of nitrogen oxides changes intermittently.
JP62131873A 1987-05-29 1987-05-29 Process for desulfurization of flue gas Granted JPS63296827A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62131873A JPS63296827A (en) 1987-05-29 1987-05-29 Process for desulfurization of flue gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62131873A JPS63296827A (en) 1987-05-29 1987-05-29 Process for desulfurization of flue gas

Publications (2)

Publication Number Publication Date
JPS63296827A JPS63296827A (en) 1988-12-02
JPH0253085B2 true JPH0253085B2 (en) 1990-11-15

Family

ID=15068134

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62131873A Granted JPS63296827A (en) 1987-05-29 1987-05-29 Process for desulfurization of flue gas

Country Status (1)

Country Link
JP (1) JPS63296827A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI580658B (en) * 2016-08-04 2017-05-01 Gfc Bioenvirotek Co Ltd The usage of fly ash from flue gas desulfurization to make compositiong for building materials

Also Published As

Publication number Publication date
JPS63296827A (en) 1988-12-02

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