JPH07185320A - Activated desulfurization and denitration method by using new flue gas treating agent - Google Patents

Activated desulfurization and denitration method by using new flue gas treating agent

Info

Publication number
JPH07185320A
JPH07185320A JP5330387A JP33038793A JPH07185320A JP H07185320 A JPH07185320 A JP H07185320A JP 5330387 A JP5330387 A JP 5330387A JP 33038793 A JP33038793 A JP 33038793A JP H07185320 A JPH07185320 A JP H07185320A
Authority
JP
Japan
Prior art keywords
earth metal
alkaline earth
treating agent
flue gas
metal carbonate
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP5330387A
Other languages
Japanese (ja)
Inventor
Tomohiro Ishizuka
朋弘 石塚
Tsutomu Ueno
務 上野
Yutaka Kitayama
裕 北山
Hiroaki Doai
宏明 土合
Hideki Nakamura
秀樹 中村
Kunihiro Mori
邦広 森
Tsutomu Yatani
勉 八谷
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 JP5330387A priority Critical patent/JPH07185320A/en
Publication of JPH07185320A publication Critical patent/JPH07185320A/en
Pending legal-status Critical Current

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

Abstract

PURPOSE:To inexpensively produce a new flue gas treating agent high in performance by adding calcium chloride to a flue gas treating agent consisting of alkaline earth metal carbonate in a specified ratio. CONSTITUTION:This new flue gas treating agent is characterized by adding 1-10wt.% of calcium chloride to a conventional treating agent consisting of alkaline earth metal carbonate. Various methods can optionally be adopted to prepare this new treating agent. For example, a powdery calcium chloride is mixed with a powdery alkaline earth metal carbonate. Or, the calcium chloride in solid, slurry or aq. soln is added to the alkaline earth metal carbonate in slurry form. Further, the slurry mixture is dried and solidified. In this way, the alkaline earth metal carbonate which have been conventionally considered to be active only at high temp. or in water can be activated even at a far lower temp.

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、従来高温あるいは水
中においてのみ有効とされているアルカリ土類金属の炭
酸塩からなる排煙処理剤の活性化方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for activating a flue gas treatment agent comprising a carbonate of an alkaline earth metal, which is conventionally effective only at high temperatures or in water.

【0002】[0002]

【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、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。
2. Description of the Related Art Sulfur oxides, nitrogen oxides, etc., contained in the exhaust gas generated by the combustion of coal, heavy oil, etc., not only harm buildings, structures, etc., but are also extremely large for animals, plants and human bodies. It has been found that it has an influence, and methods for removing the above substances in exhaust gas, that is, desulfurization and denitration methods have been studied, and various methods have been developed.

【0003】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。
The desulfurization method is roughly classified into a dry method, a semi-dry method and a wet method. The methods shown in Table 1 are known as the dry method and the semi-dry method to which the present invention belongs.

【0004】[0004]

【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。
[Table 1] In the absorption method shown in Table 1, expensive NH 3 is required for the regeneration of the reactant (sulfur or sulfur compound recovery) (active manganese oxide method), or a valuable reducing gas is required (Alkalisation). Doalumina method) or high reaction temperature (alkalized alumina method, lime blowing method).

【0005】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。
The adsorption method has drawbacks in that the activated carbon used is expensive and easily deteriorates. In the catalytic oxidation method, the vanadium-based catalyst used is expensive and easily deteriorates, and the reaction temperature is relatively high. There is a point.

【0006】一方、半乾式脱硫法は、Ca(OH)2
吸収剤とする方式が主体であり、乾式法、湿式石灰石石
膏法(以下湿式法と略記)に比べて簡易、低コストでは
あるが脱硫性能が低いという点と、高価なCa(OH)
2を使用することによるランニングコストの上昇などの
問題点がある。
On the other hand, the semi-dry desulfurization method mainly uses Ca (OH) 2 as an absorbent, and is simpler and less expensive than the dry method and wet limestone gypsum method (hereinafter abbreviated as wet method). Is low in desulfurization performance and expensive Ca (OH)
There are problems such as an increase in running cost due to the use of 2 .

【0007】[0007]

【発明が解決しようとする課題】この発明の目的は、ア
ルカリ土類金属の炭酸塩の脱硫、脱硝能力を活性化する
ことによって、従来の乾式および半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と脱硫、脱
硝方法を提供することにある。
SUMMARY OF THE INVENTION An object of the present invention is to solve various problems of conventional dry and semi-dry desulfurization methods by activating desulfurization and denitrification ability of alkaline earth metal carbonates. The purpose is to provide an inexpensive and high-performance flue gas treatment agent and a desulfurization and denitration method.

【0008】[0008]

【課題を解決するための手段】この発明はアルカリ土類
金属炭酸塩よりなる排煙処理剤に、塩化カルシウムを1
〜10重量%添加することを特徴とする排煙処理剤の脱
硫、脱硝活性化法である。
According to the present invention, a flue gas treating agent comprising an alkaline earth metal carbonate and calcium chloride
It is a desulfurization and denitration activation method for a flue gas treatment agent, which is characterized by adding 10 to 10% by weight.

【0009】半乾式または乾式法で利用されているCa
(OH)2 は、次に示す式(1)または(2)のように
反応していると考えられる。
Ca used in the semi-dry or dry method
It is considered that (OH) 2 reacts as shown in the following formula (1) or (2).

【0010】 Ca(OH)2 +SO2 →CaSO3 +H2 O…(1) Ca(OH)2 +SO2 +1/202 →CaSO4+H2 O…(2) この発明における排煙処理剤は、主成分がアルカリ土類
金属炭酸塩であるにもかかわらず、式(1),(2)と
同様の反応が式(3),(4)に示すように進み、アル
カリ土類金属硫酸塩または亜硫酸塩として排ガス中のS
2 を固定化、除去することができる。
Ca (OH) 2 + SO 2 → CaSO 3 + H 2 O ... (1) Ca (OH) 2 + SO 2 +1/20 2 → CaSO 4 + H 2 O ... (2) Even though the main component is alkaline earth metal carbonate, the same reactions as in formulas (1) and (2) proceed as shown in formulas (3) and (4), and alkaline earth metal sulfate or S in the exhaust gas as sulfite
O 2 can be fixed and removed.

【0011】 CaCO3 +SO2 →CaSO3 +CO2 …(3) CaCO3 +SO2+1/202 →CaSO4 +CO2 …(4) 従来、アルカリ土類金属炭酸塩は、排ガス中のSO2
の反応性が低いことから、主に700〜800℃以上の
高温域(炉内脱硫法)あるいは水中においてSO2 と反
応(温式法)すると考えられていた。本発明は、塩化カ
ルシウムを添加することにより気相においても比較的低
温でSO2 を除去できる排煙処理剤を提供することがで
きる。
[0011] CaCO 3 + SO 2 → CaSO 3 + CO 2 ... (3) CaCO 3 + SO 2 +1/20 2 → CaSO 4 + CO 2 ... (4) Conventionally, an alkaline earth metal carbonate, with SO 2 in the flue gas Due to its low reactivity, it has been thought that it mainly reacts with SO 2 in a high temperature range of 700 to 800 ° C. or higher (in-furnace desulfurization method) or water (thermal method). The present invention can provide a flue gas treatment agent capable of removing SO 2 at a relatively low temperature even in the gas phase by adding calcium chloride.

【0012】この発明でアルカリ土類金属炭酸塩は、そ
のアルカリ土類金属の種類がカルシウムおよびマグネシ
ウムであり、実際使用する原料としては、石灰石、炭酸
カルシウム、炭酸マグネシウム、ドロマイト、セメン
ト、スラグ、使用済脱硫剤等のアルカリ土類金属炭酸塩
を含有する物質等が挙げられる。
In the present invention, the alkaline earth metal carbonate has calcium and magnesium as the alkaline earth metal, and the raw materials to be actually used are limestone, calcium carbonate, magnesium carbonate, dolomite, cement, slag, and used. Examples thereof include substances containing an alkaline earth metal carbonate such as a desulfurizing agent.

【0013】アルカリ土類金属炭酸塩に対する塩化カル
シウムの添加割合は重量比で100:1〜10が好まし
い。添加量が1%未満であれば、添加効果の発現が充分
でなく、10%を超えても添加の効果は上がらない。
The addition ratio of calcium chloride to the alkaline earth metal carbonate is preferably 100: 1 to 10 by weight. If the addition amount is less than 1%, the effect of addition is not sufficiently exhibited, and if it exceeds 10%, the effect of addition is not improved.

【0014】添加の方法としては、両者を粉状として混
合する方法、粉砕と混合を同時に行う方法、アルカリ土
類金属炭酸塩のスラリーに、固体、スラリー、または水
溶液とした塩化カルシウムを添加する方法等、任意の方
法が採用できる。添加操作に水を使用する場合の、混合
後の水分量は、乾物100重量部あたり10〜500重
量部が適当である。添加後必要により乾燥し、固化し、
あるいは公知の方法で粒状化する。乾燥条件は、50〜
500℃で数秒〜10時間が好ましい。
As a method of addition, a method of mixing both in a powder form, a method of simultaneously pulverizing and mixing, a method of adding calcium chloride in the form of a solid, a slurry or an aqueous solution to a slurry of an alkaline earth metal carbonate. Etc., any method can be adopted. When water is used for the adding operation, the amount of water after mixing is appropriately 10 to 500 parts by weight per 100 parts by weight of dry matter. After addition, if necessary, dry and solidify,
Alternatively, it is granulated by a known method. Drying condition is 50 ~
It is preferably several seconds to 10 hours at 500 ° C.

【0015】上記の添加方法により得られた混合物は、
スラリー、粉、粒状で排煙処理剤として使用することが
できる。
The mixture obtained by the above addition method is
It can be used as a smoke treatment agent in the form of slurry, powder or granules.

【0016】スラリーで用いる場合は、処理すべき排煙
の通る煙道あるいはスプレードライヤー内に噴霧し、バ
グフィルターのような公知の集塵装置で捕集排出する。
When it is used as a slurry, it is sprayed into a flue passage through which the exhaust gas to be treated passes or a spray dryer, and is collected and discharged by a known dust collecting device such as a bag filter.

【0017】粉状で用いる場合もスラリーに準じて行う
か、流動層あるいは噴流層に供給する方法も採用でき
る。粒状のものを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型し移動層、固定
層、流動層、噴流層において使用することができる。
When it is used in the form of powder, it may be carried out in accordance with the slurry, or a method of supplying it to a fluidized bed or a spouted bed can be adopted. When a granular material is used, a powdery material can be molded by a known method such as a disk pelleter and used in a moving bed, a fixed bed, a fluidized bed or a spouted bed.

【0018】排ガスの処理温度は室温〜300℃、好ま
しくは60〜250℃である。
The treatment temperature of the exhaust gas is room temperature to 300 ° C, preferably 60 to 250 ° C.

【0019】[0019]

【実施例】 実施例1 市販の炭酸カルシウムに水を加え、スラリー濃度を1
6.7%とし、95℃に保持して市販の塩化カルシウム
を表2に示した割合で添加し、30分攪拌した後、20
0℃で2時間乾燥させて排煙処理剤を得た。これらの剤
を用いて表3に示した試験条件で性能評価試験を行い、
5時間後の脱硫率、脱硝率を求めて表2に示した。
Example 1 Water was added to commercially available calcium carbonate to adjust the slurry concentration to 1
It was adjusted to 6.7% and kept at 95 ° C., and commercially available calcium chloride was added at the ratio shown in Table 2, and after stirring for 30 minutes, 20
It was dried at 0 ° C. for 2 hours to obtain a flue gas treatment agent. A performance evaluation test was conducted using these agents under the test conditions shown in Table 3,
The desulfurization rate and the denitration rate after 5 hours were obtained and shown in Table 2.

【0020】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 measurement results of the specific surface area are also shown in the table. The specific surface area was measured by the BET method after degassing the sample at 300 ° C. for 1 hour.

【0021】実施例2 市販の炭酸マグネシウムを濃度16.7%のスラリーと
し、95℃に保持し、市販の塩化カルシウムを表2に示
した割合で添加し、30分攪拌した後、200℃で2時
間乾燥させ、表3に示した条件で性能評価試験を行い、
結果を表2に示した。
Example 2 Commercially available magnesium carbonate was made into a slurry having a concentration of 16.7%, kept at 95 ° C., commercially available calcium chloride was added at the ratio shown in Table 2, and after stirring for 30 minutes, at 200 ° C. It is dried for 2 hours, and a performance evaluation test is conducted under the conditions shown in Table 3,
The results are shown in Table 2.

【0022】実施例3 市販の石灰石を200メッシュ以下に粉砕したものと市
販の塩化カルシウムとを表2に示した割合で粉体同士で
混合し、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2に示した。
Example 3 Commercially available limestone pulverized to 200 mesh or less and commercially available calcium chloride were mixed with each other at a ratio shown in Table 2 to obtain an flue gas treatment agent. The same performance evaluation test as in Example 1 was performed, and the results are shown in Table 2.

【0023】実施例4 95℃に保持された石灰石スラリーに市販の塩化カルシ
ウムを表2に示した割合で添加し、30分攪拌した後、
200℃で2時間乾燥して排煙処理剤を得た。前例と同
様の性能評価試験を行い、結果を表2に示した。
Example 4 Commercially available calcium chloride was added to the limestone slurry kept at 95 ° C. in the ratio shown in Table 2, and after stirring for 30 minutes,
It was dried at 200 ° C. for 2 hours to obtain a flue gas treating agent. The same performance evaluation test as in the previous example was conducted, and the results are shown in Table 2.

【0024】比較例1 実施例1において、塩化カルシウムの添加を除いて同じ
操作で得た炭酸カルシウム単体の試料について性能評価
試験を行い、その結果を表2に示した。
Comparative Example 1 A performance evaluation test was conducted on a sample of calcium carbonate alone obtained by the same operation as in Example 1 except that calcium chloride was not added, and the results are shown in Table 2.

【0025】比較例2 実施例2において、塩化カルシウムの添加を除いて同じ
操作で得た炭酸マグネシウム単体の試料について性能評
価試験を行い、その結果を表2に示した。
Comparative Example 2 A performance evaluation test was conducted on a sample of magnesium carbonate alone obtained by the same procedure as in Example 2 except that calcium chloride was not added, and the results are shown in Table 2.

【0026】比較例3 市販の塩化カルシウムについて実施例1と同じ条件で性
能評価試験を行ったがいずれの温度条件においても脱硫
・脱硝に関する活性は認められなかった。
Comparative Example 3 Commercially available calcium chloride was subjected to a performance evaluation test under the same conditions as in Example 1, but no activity related to desulfurization and denitration was observed under any temperature condition.

【0027】[0027]

【表2】 [Table 2]

【0028】[0028]

【表3】 *炭酸マグネシウム系は30g 炭酸カルシウム系は60g[Table 3] * Magnesium carbonate type is 30g and calcium carbonate type is 60g

【0029】[0029]

【発明の効果】この発明によれば、従来高温あるいは水
中でのみ活性があるとされたアルカリ土類金属炭酸塩を
活性化して、はるかに低温で活性のある排煙処理剤を提
供することが可能になった。
According to the present invention, it is possible to provide an flue gas treatment agent which is active at a much lower temperature by activating an alkaline earth metal carbonate which was conventionally considered to be active only at a high temperature or in water. It became possible.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/74 C01F 11/46 9040−4G (72)発明者 土合 宏明 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 (72)発明者 中村 秀樹 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 (72)発明者 森 邦広 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 (72)発明者 八谷 勉 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─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/74 C01F 11/46 9040-4G (72) Inventor Hiroaki Doi 4 Migamioka, Toyohira-ku, Sapporo-shi, Hokkaido Article 9-2-1 No. 1 in Hokkaido Electric Power Co., Inc. Research Institute (72) Inventor Hideki Nakamura 4-9-2, Miyoshioka, Toyohira-ku, Sapporo, Hokkaido Hokkaido Electric Power Co., Inc. Research Institute (72) Inventor Kunihiro Mori Hokkaido Sapporo City Toyohira-ku Mihogaoka 4-92-1 Hokkaido Research Institute of Electric Power Company (72) Inventor Tsutomu Yatani Hokkaido Mihogaoka Mihogaoka 4-92-1 Hokkaido Electric Power Company Research Institute

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 アルカリ土類金属炭酸塩よりなる排煙処
理剤に、塩化カルシウムを1〜10重量%添加すること
を特徴とする排煙処理剤の脱硫、脱硝活性化法。
1. A method for desulfurization and denitration activation of a flue gas treating agent, which comprises adding 1 to 10% by weight of calcium chloride to the flue gas treating agent composed of an alkaline earth metal carbonate.
【請求項2】 粉状アルカリ土類金属炭酸塩に粉状塩化
カルシウムを混合して添加する請求項1記載の活性化
法。
2. The activation method according to claim 1, wherein powdery calcium carbonate is mixed with powdery alkaline earth metal carbonate and added.
【請求項3】 アルカリ土類金属炭酸塩をスラリー状と
し、固体、スラリー状または水溶液とした塩化カルシウ
ムを添加する請求項1記載の活性化法。
3. The activation method according to claim 1, wherein the alkaline earth metal carbonate is slurried and calcium chloride in a solid, slurry or aqueous solution is added.
【請求項4】 添加生成したスラリーをさらに乾燥、固
化する請求項3記載の活性化法。
4. The activation method according to claim 3, wherein the added slurry is further dried and solidified.
JP5330387A 1993-12-27 1993-12-27 Activated desulfurization and denitration method by using new flue gas treating agent Pending JPH07185320A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5330387A JPH07185320A (en) 1993-12-27 1993-12-27 Activated desulfurization and denitration method by using new flue gas treating agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5330387A JPH07185320A (en) 1993-12-27 1993-12-27 Activated desulfurization and denitration method by using new flue gas treating agent

Publications (1)

Publication Number Publication Date
JPH07185320A true JPH07185320A (en) 1995-07-25

Family

ID=18232037

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5330387A Pending JPH07185320A (en) 1993-12-27 1993-12-27 Activated desulfurization and denitration method by using new flue gas treating agent

Country Status (1)

Country Link
JP (1) JPH07185320A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010064607A1 (en) * 2008-12-01 2010-06-10 Oyama Terutsugu Treatment method and treatment device for sulfurous acid gas in thermal power generation

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010064607A1 (en) * 2008-12-01 2010-06-10 Oyama Terutsugu Treatment method and treatment device for sulfurous acid gas in thermal power generation

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