JPS6255891B2 - - Google Patents
Info
- Publication number
- JPS6255891B2 JPS6255891B2 JP58186388A JP18638883A JPS6255891B2 JP S6255891 B2 JPS6255891 B2 JP S6255891B2 JP 58186388 A JP58186388 A JP 58186388A JP 18638883 A JP18638883 A JP 18638883A JP S6255891 B2 JPS6255891 B2 JP S6255891B2
- Authority
- JP
- Japan
- Prior art keywords
- type hemihydrate
- hemihydrate gypsum
- reactor
- flue gas
- gypsum
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/46—Sulfates
- C01F11/464—Sulfates of Ca from gases containing sulfur oxides
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Inorganic Chemistry (AREA)
- Treating Waste Gases (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
Description
本発明は、α型半水石こうの製造と排煙脱硫と
を経済的に行うことができる方法に関するもので
ある。
従来から、特公昭51−43833号公報に示される
ように、湿式脱硫装置の酸化塔後段にα型半水石
こう反応器を設備したα型半水石こうの製造方法
が公知であるが、この方法において、実用になる
結晶形の良好なα型半水石こうを製造するために
は、反応液中に媒晶剤を添加する必要がある。反
応液は脱硫装置へ戻され、循環使用されるので、
添加された媒晶剤は脱硫反応に影響を与えてしま
う。すなわち、α型半水石こう製造に、通常用い
られる有機系媒晶剤を使用した場合、熱で劣化し
た有機物が脱硫系内に蓄積して種々の悪影響を与
える。
α型半水石こう反応器は液中にて反応させ、熱
経済上、液はリサイクルして使用または熱交換し
て使用することになるが、液の組成は厳重に管理
する必要がある。排煙脱硫装置の液とα型半水石
こう反応器の液の組成が相違する場合には、各々
の液が他方の系の反応を阻害しないように、2水
石こうを液から分離して(含液ケーク状で)α型
半水石こう反応器に送る必要がある。さらにケー
ク含液中の有害物質を除去する装置が必要になる
場合さえある。排煙脱硫装置の中にα型半水石こ
う反応器を組み込んだ場合は、それぞれの液が混
じることになる。上記従来のα型半水石こう製造
装置は有機媒晶剤を使用するため、脱硫排液の
COD増大、脱硫性能への影響、その他の反応へ
の影響を始めとし、多くの問題が生じる。
本発明は上記の諸点に鑑みなされたもので、カ
ルシウム化合物を主体とする吸収剤を用いる湿式
排煙脱硫装置における酸化塔の後流にα型半水石
こう反応器を設け、この反応器に湿式排煙脱硫装
置で生じた2水石こうスラリーを供給してα型半
水石こうを製造する方法において、カルシウム化
合物を主体とする吸収剤に予めマグネシウム化合
物を添加し、この吸収剤を用いて排煙脱硫処理
し、生成した硫酸マグネシウムを含有するスラリ
ーをそのままα型半水石こう反応器に導入するこ
とにより、または酸化塔から排出される硫酸マグ
ネシウムを含有する2水石こうスラリー中の含有
空気を分離し、2水石こうスラリー濃度を十分に
高めた後、α型半水石こう反応器に導入すること
により、α型半水石こう反応器からの液を排煙脱
硫装置に戻しても何ら副作用を生じないα型半水
石こうの副生を伴う排煙脱硫方法を提供せんとす
るものである。
以下、本発明の構成を図面に基づいて説明す
る。まず主要な吸収剤である消石灰または炭酸カ
ルシウム(以下、消石灰という)が、スラリー調
整槽1に投入され、ここで酸化塔2から排出され
たスラリーと混合される。また全系内のマグネシ
ウム濃度を一定値に維持するための水酸化マグネ
シウムもこのスラリー調整槽1に投入される。ス
ラリー調整槽1内で、消石灰の一部は酸化スラリ
ー中の硫酸マグネシウムと反応して、水酸化マグ
ネシウムに転換される。スラリー調整槽1のスラ
リーは吸収塔3に送られる。吸収塔スラリーは塔
内にスプレーされて排ガスと接触し、ガス中の
SO2をつぎの反応により吸収する。
Ca(OH)2+SO2→CaSO3+H2O
Mg(OH)2+SO2→MgSO3+H2O
吸収により生じた亜硫酸カルシウムと亜硫酸マ
グネシウムは、つぎの反応により一部がガス中の
酸素により酸化され、石こうと硫酸マグネシウム
になる。
CaSO3+1/2O2→CaSO4(2水塩)
MgSO3+1/2O2→MgSO4(溶液)
この酸化反応を完全にするために、吸収塔3か
らのスラリーは酸化塔2に送られ、そこで空気が
吹込まれる。酸化塔2から排出される酸化塔スラ
リーは、一部がスラリー調整槽1に送られ残部は
シツクナー4に送られて、濃縮スラリーと上澄液
に分けられる。上澄液は吸収塔3に戻され、濃縮
スラリーは熱交換器5で予熱された後、α型半水
石こう反応器6に送られる。α型半水石こう反応
器6では、スラリーは蒸気吹込により高温に一定
時間保持され、スラリー中の2水石こうはα型半
水石こうに転換される。α型半水石こう反応器6
から出たスラリーは、フラツシユして常圧に戻し
た後、直ちに固液分離器7にかけられる。固形分
は乾燥機8により短時間のうちに乾燥されて、製
品α型半水石こうとなる。液分は熱交換器5で、
前記シツクナー4からの濃縮スラリーの予熱用熱
源として使用された後、吸収塔3に戻される。
以上説明したように本発明の方法によれば、つ
ぎのような効果を奏する。
(1) 脱硫装置の母液中の硫酸マグネシウムは、本
来、脱硫効果を高めるために添加しているもの
であるが、これをそのままα型半水石こう生成
反応の媒晶剤として利用することができる。す
なわちα型半水石こう反応器の母液は脱硫装置
の母液をそのまま使えば良く、改めて媒晶剤を
加える必要はない。反応器中の硫酸マグネシウ
ム濃度を一定値に管理する必要があるが、脱硫
装置の脱硫反応のために、既に調整されている
ので、とくに再調整しなくて良い。このように
排煙脱硫装置の液とα型半水石こう反応器の液
とは共用され、かつどちらも機能、性能とも互
に阻害することなく運転が可能であり、前述の
従来方式の問題を全く生じないで、簡単で合理
的な方法である。
(2) 脱硫装置から2水石こうの脱水装置、搬送装
置を省略することができる。
(3) 酸化塔出口において、一旦、石こうスラリー
中の含有空気を充分に分離し、かつ石こうスラ
リー濃度を高くする場合は、α型半水石こう反
応器における加熱に要する熱消費量を大幅に減
少することができる。
つぎに本発明の実施例について説明する。
実施例
温度150℃、SOx濃度1500ppm(ドライベー
ス)の重油焚ボイラ排ガスを図面に示すフローに
従つて処理した。清浄ガスの温度は55℃、SOx濃
度は200ppm(ドライベース)であつた。また酸
化塔出口の液は、MgSO4濃度が6wt%、スラリー
濃度が7wt%であり、α型半水石こう反応器内の
液は、MgSO4濃度が6wt%、スラリー濃度が20wt
%、PHが5〜7、温度が120℃、滞留時間が4時
間であつた。得られたα型半水石こうの性状は次
表に示す如くであつた。
The present invention relates to an economical method for producing α-type hemihydrate gypsum and flue gas desulfurization. Conventionally, as shown in Japanese Patent Publication No. 51-43833, a method for producing α-type hemihydrate gypsum is known in which an α-type hemihydrate gypsum reactor is installed after the oxidation tower of a wet desulfurization equipment. In order to produce α-type hemihydrate gypsum with a good crystalline shape for practical use, it is necessary to add a crystal modifier to the reaction solution. The reaction liquid is returned to the desulfurization equipment and used for circulation.
The added crystal modifier will affect the desulfurization reaction. That is, when a commonly used organic crystal modifier is used in the production of α-type hemihydrate gypsum, organic substances degraded by heat accumulate in the desulfurization system, causing various adverse effects. In the α-type hemihydrate gypsum reactor, the reaction is carried out in a liquid, and from a thermoeconomic perspective, the liquid can be recycled or used for heat exchange, but the composition of the liquid must be strictly controlled. If the composition of the liquid in the flue gas desulfurization equipment and the liquid in the α-type hemihydrate gypsum reactor is different, separate the dihydrate gypsum from the liquid so that each liquid does not inhibit the reaction of the other system. (in the form of a liquid-containing cake) must be sent to an α-type hemihydrate gypsum reactor. Furthermore, equipment for removing harmful substances from the cake liquid may even be required. When an α-type hemihydrate gypsum reactor is incorporated into a flue gas desulfurization equipment, the respective liquids will be mixed. The conventional α-type hemihydrate gypsum production equipment described above uses an organic modifier, so the desulfurization wastewater is
Many problems arise, including increased COD, effects on desulfurization performance, and effects on other reactions. The present invention was made in view of the above points, and includes an α-type hemihydrate gypsum reactor installed downstream of the oxidation tower in a wet flue gas desulfurization equipment using an absorbent mainly containing calcium compounds. In the method of producing α-type hemihydrate gypsum by supplying dihydrate gypsum slurry generated in flue gas desulfurization equipment, a magnesium compound is added in advance to an absorbent mainly composed of calcium compounds, and this absorbent is used to remove flue gas. By introducing the desulfurized slurry containing magnesium sulfate as it is into an α-type hemihydrate gypsum reactor, or by separating the air contained in the dihydrate gypsum slurry containing magnesium sulfate discharged from the oxidation tower. By introducing the dihydrate gypsum slurry into the α-type hemihydrate gypsum reactor after sufficiently increasing the concentration, no side effects will occur even if the liquid from the α-type hemihydrate gypsum reactor is returned to the flue gas desulfurization equipment. The present invention aims to provide a flue gas desulfurization method that involves the by-production of α-type hemihydrate gypsum. Hereinafter, the configuration of the present invention will be explained based on the drawings. First, slaked lime or calcium carbonate (hereinafter referred to as slaked lime), which is a main absorbent, is put into the slurry adjustment tank 1, where it is mixed with the slurry discharged from the oxidation tower 2. Magnesium hydroxide is also charged into the slurry adjustment tank 1 in order to maintain the magnesium concentration in the entire system at a constant value. In the slurry conditioning tank 1, a portion of the slaked lime reacts with magnesium sulfate in the oxidized slurry and is converted to magnesium hydroxide. The slurry in the slurry adjustment tank 1 is sent to an absorption tower 3. The absorption tower slurry is sprayed into the tower and comes into contact with the flue gas, and the
SO 2 is absorbed by the following reaction. Ca(OH) 2 +SO 2 →CaSO 3 +H 2 O Mg(OH) 2 +SO 2 →MgSO 3 +H 2 O Calcium sulfite and magnesium sulfite produced by absorption are partially oxidized by oxygen in the gas in the following reaction. and becomes gypsum and magnesium sulfate. CaSO 3 +1/2O 2 →CaSO 4 (dihydrate) MgSO 3 +1/2O 2 →MgSO 4 (solution) In order to complete this oxidation reaction, the slurry from absorption tower 3 is sent to oxidation tower 2, Air is blown in there. A part of the oxidizing tower slurry discharged from the oxidizing tower 2 is sent to the slurry adjustment tank 1, and the rest is sent to the thickener 4, where it is divided into a concentrated slurry and a supernatant liquid. The supernatant liquid is returned to the absorption tower 3, and the concentrated slurry is preheated in a heat exchanger 5 and then sent to an α-type hemihydrate gypsum reactor 6. In the α-type hemihydrate gypsum reactor 6, the slurry is maintained at a high temperature for a certain period of time by steam injection, and dihydrate gypsum in the slurry is converted to α-type hemihydrate gypsum. α type hemihydrate gypsum reactor 6
The slurry discharged from the tank is flashed and returned to normal pressure, and then immediately applied to the solid-liquid separator 7. The solid content is dried in a short time by the dryer 8 to become a product α-type hemihydrate gypsum. The liquid is transferred to heat exchanger 5.
After being used as a heat source for preheating the concentrated slurry from the thickener 4, it is returned to the absorption tower 3. As explained above, the method of the present invention provides the following effects. (1) Magnesium sulfate in the mother liquor of the desulfurization equipment is originally added to enhance the desulfurization effect, but it can be used as is as a modifier for the α-type hemihydrate gypsum production reaction. . That is, the mother liquor of the α-type hemihydrate gypsum reactor can be used as it is from the desulfurizer, and there is no need to add a crystal modifier. Although it is necessary to control the magnesium sulfate concentration in the reactor to a constant value, it has already been adjusted for the desulfurization reaction in the desulfurization device, so there is no need to readjust it. In this way, the fluid in the flue gas desulfurization equipment and the fluid in the α-type hemihydrous gypsum reactor are shared, and both can be operated without interfering with each other's functions and performance, eliminating the problems of the conventional method mentioned above. It is a simple and reasonable method that does not occur at all. (2) It is possible to omit the dihydrate gypsum dehydration device and conveyance device from the desulfurization device. (3) Once the air contained in the gypsum slurry is sufficiently separated at the oxidation tower outlet and the gypsum slurry concentration is increased, the heat consumption required for heating in the α-type hemihydrate gypsum reactor can be significantly reduced. can do. Next, embodiments of the present invention will be described. Example Heavy oil-fired boiler exhaust gas with a temperature of 150°C and an SOx concentration of 1500 ppm (dry base) was treated according to the flow shown in the drawing. The temperature of the clean gas was 55°C, and the SOx concentration was 200 ppm (dry basis). In addition, the liquid at the outlet of the oxidation tower has a MgSO 4 concentration of 6wt% and a slurry concentration of 7wt%, and the liquid in the α-type hemihydrate gypsum reactor has a MgSO 4 concentration of 6wt% and a slurry concentration of 20wt%.
%, pH was 5-7, temperature was 120°C, and residence time was 4 hours. The properties of the obtained α-type hemihydrate gypsum were as shown in the following table.
【表】【table】
【表】
以上のことから明らかなように、十分な脱硫性
能を維持しながら、良好なα型半水石こうを得る
ことができた。[Table] As is clear from the above, good α-type hemihydrate gypsum could be obtained while maintaining sufficient desulfurization performance.
図面は本発明のα型半水石こうの副生を伴う排
煙脱硫方法を実施する装置の一例を示すフローシ
ートである。
1……スラリー調整槽、2……酸化塔、3……
吸収塔、4……シツクナー、5……熱交換器、6
……α型半水石こう反応器、7……固液分離器、
8……乾燥器。
The drawing is a flow sheet showing an example of an apparatus for carrying out the flue gas desulfurization method involving the by-production of α-type hemihydrate gypsum of the present invention. 1... Slurry adjustment tank, 2... Oxidation tower, 3...
Absorption tower, 4...Sickener, 5...Heat exchanger, 6
...α-type hemihydrate gypsum reactor, 7... solid-liquid separator,
8...Dryer.
Claims (1)
る湿式排煙脱硫装置における酸化塔の後流にα型
半水石こう反応器を設け、この反応器に湿式排煙
脱硫装置で生じた2水石こうスラリーを供給して
α型半水石こうを製造する方法において、カルシ
ウム化合物を主体とする吸収剤に予めマグネシウ
ム化合物を添加し、この吸収剤を用いて排煙脱硫
処理し、生成した硫酸マグネシウムを含有するス
ラリーをそのままα型半水石こう反応器に導入す
ることを特徴とするα型半水石こうの副生を伴う
排煙脱硫方法。 2 カルシウム化合物を主体とする吸収剤を用い
る湿式排煙脱硫装置における酸化塔の後流にα型
半水石こう反応器を設け、この反応器に湿式排煙
脱硫装置で生じた2水石こうスラリーを供給して
α型半水石こうを製造する方法において、カルシ
ウム化合物を主体とする吸収剤に予めマグネシウ
ム化合物を添加し、酸化塔から排出される硫酸マ
グネシウムを含有する2水石こうスラリー中の含
有空気を分離し、2水石こうスラリー濃度を十分
に高めた後、α型半水石こう反応器に導入するこ
とを特徴とするα型半水石こうの副生を伴う排煙
脱硫方法。[Scope of Claims] 1. An α-type hemihydrous gypsum reactor is installed downstream of the oxidation tower in a wet flue gas desulfurization system using an absorbent mainly containing a calcium compound, and this reactor is equipped with a In the method of producing α-type hemihydrate gypsum by supplying dihydrate gypsum slurry, a magnesium compound is added in advance to an absorbent mainly composed of calcium compounds, and this absorbent is used to perform flue gas desulfurization treatment to produce α-type hemihydrate gypsum. A flue gas desulfurization method accompanied by by-product of α-type hemihydrate gypsum, characterized by introducing a slurry containing magnesium sulfate as it is into an α-type hemihydrate gypsum reactor. 2. An α-type hemihydrate gypsum reactor is installed downstream of the oxidation tower in a wet flue gas desulfurization equipment that uses an absorbent mainly composed of calcium compounds, and the dihydrate gypsum slurry produced in the wet flue gas desulfurization equipment is fed to this reactor. In the method of producing α-type hemihydrate gypsum by supplying it, a magnesium compound is added in advance to an absorbent mainly composed of calcium compounds, and the air contained in the dihydrate gypsum slurry containing magnesium sulfate discharged from the oxidation tower is removed. A flue gas desulfurization method accompanied by by-product of α-type hemihydrate gypsum, which is characterized in that the dihydrate gypsum slurry is separated and sufficiently increased in concentration, and then introduced into an α-type hemihydrate gypsum reactor.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58186388A JPS6078621A (en) | 1983-10-05 | 1983-10-05 | Waste gas desulfurizing method accompanying formation of byproduct alpha type gypsum hemihydrate |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58186388A JPS6078621A (en) | 1983-10-05 | 1983-10-05 | Waste gas desulfurizing method accompanying formation of byproduct alpha type gypsum hemihydrate |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6078621A JPS6078621A (en) | 1985-05-04 |
| JPS6255891B2 true JPS6255891B2 (en) | 1987-11-21 |
Family
ID=16187514
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58186388A Granted JPS6078621A (en) | 1983-10-05 | 1983-10-05 | Waste gas desulfurizing method accompanying formation of byproduct alpha type gypsum hemihydrate |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6078621A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH048395U (en) * | 1990-05-11 | 1992-01-24 |
-
1983
- 1983-10-05 JP JP58186388A patent/JPS6078621A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH048395U (en) * | 1990-05-11 | 1992-01-24 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6078621A (en) | 1985-05-04 |
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