JPS5870876A - Purifying treatment of desulfurizing waste liquid for coke oven gas - Google Patents
Purifying treatment of desulfurizing waste liquid for coke oven gasInfo
- Publication number
- JPS5870876A JPS5870876A JP56169514A JP16951481A JPS5870876A JP S5870876 A JPS5870876 A JP S5870876A JP 56169514 A JP56169514 A JP 56169514A JP 16951481 A JP16951481 A JP 16951481A JP S5870876 A JPS5870876 A JP S5870876A
- Authority
- JP
- Japan
- Prior art keywords
- na2so4
- waste liquid
- coke oven
- oven gas
- gas
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
Landscapes
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
Abstract
Description
【発明の詳細な説明】
この発明はコークス炉ガス(OOG)脱硫廃液(J
主としチオシアン酸ナトリウム、チオ亜硫酸ナトリウム
、硫酸ナトリウムを含む)の処理方法に関するものであ
る
石炭を乾留して得られる;−クス炉ガスを燃料として使
用する場合、大気汚染の原因となる硫黄化合物(主とし
て硫化水素)及び窒素化合物(主としてアンモニア)、
シアン化水素等の除去が必要となる。従来これら硫化水
素、シアン化水素及びアンモニアの除去方法に関しては
、公知の吸収法による除去方法が工業化されており、こ
の中で硫化水素及びシアン化水素の除去方法としては、
アルカリを用いて除去するタカハックス法、ロダックス
法、フマックス法等がすでに知られている。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating coke oven gas (OOG) desulfurization waste liquid (J mainly containing sodium thiocyanate, sodium thiosulfite, and sodium sulfate) obtained by carbonizing coal; - When using coffer oven gas as fuel, sulfur compounds (mainly hydrogen sulfide) and nitrogen compounds (mainly ammonia) that cause air pollution;
Removal of hydrogen cyanide, etc. is required. Conventionally, methods for removing hydrogen sulfide, hydrogen cyanide, and ammonia have been industrialized using known absorption methods.
Takahax method, Rodax method, Fumax method, etc., which use alkali for removal, are already known.
上記方法に於いてアルカリとして特に炭酸ナトリウムを
用いるソーダタカハックス法の場合には、シアン化水素
はチオシアン酸ナトリウム(Na$gN)として固定さ
れる。また硫化水素は炭酸ナトリウムと反応して水硫化
ナトリウム(NaHJG)となるが、このものは酸化還
元触媒を用いる事により単体硫黄として固定すゐことが
できる。この反応では触媒は酸化反応により再生されこ
の場合水硫化ナトリウムの一部は、酸化されてチオ亜硫
酸ナトリウム(N* 1% Os )及び硫酸ナトリウ
ムCNaa Boa )が副生ずる。この様にして発生
したチオシアン酸ナトリウム、チオ亜硫酸ナトリウム、
硫酸ナトリウムは、脱硫、脱シアン反応には寄与せず循
環系内に蓄積して行くので、吸収液の一部を常に抜いて
副生し丸環を除去しなければならない。この抜き出され
た上記3成分を主とする廃液の処理方法については、公
知の技術としていくつかの方法がすでに工業化されてい
る。その中の1つに環元燃焼分解法があり、この方法は
廃液を補助燃料と混焼し空気率α9以下で、かつ燃焼ガ
ス温度700℃以上1100℃以下の所定の条件下で行
なって廃液中の硫黄化合物塩を熱分解せしめ、生成され
た硫化水素およびアルカリ炭酸塩を燃焼ガスと共に水と
直接接触させることによシ、アルカリ炭酸塩は水溶液と
して回収し循環使用すると共に硫化水素を排出ガス中に
得る。この方法の運転には、補助燃料及び燃料供給設備
、空気供給設備等多大のエネルー−を必要とし、また発
生する燃焼ガス中には高濃度の硫化水素が含まれている
ために再脱硫e儂を要する等の欠点を有している。In the case of the Soda Takahax method in which sodium carbonate is used as the alkali in the above method, hydrogen cyanide is fixed as sodium thiocyanate (Na$gN). Further, hydrogen sulfide reacts with sodium carbonate to form sodium hydrosulfide (NaHJG), which can be fixed as elemental sulfur by using a redox catalyst. In this reaction, the catalyst is regenerated by an oxidation reaction, in which part of the sodium hydrosulfide is oxidized to produce by-products sodium thiosulfite (N* 1% Os ) and sodium sulfate (CNaa Boa ). Sodium thiocyanate, sodium thiosulfite, and
Sodium sulfate does not contribute to desulfurization and decyanization reactions and accumulates in the circulation system, so a portion of the absorption liquid must be constantly removed to remove the by-product circular rings. Several methods have already been commercialized as known techniques for treating the extracted waste liquid mainly containing the above three components. One of these methods is the cyclic combustion decomposition method, in which the waste liquid is co-combusted with auxiliary fuel, the air ratio is α9 or less, and the combustion gas temperature is 700°C or higher and 1100°C or lower. By thermally decomposing the sulfur compound salts and bringing the generated hydrogen sulfide and alkali carbonate into direct contact with water together with the combustion gas, the alkali carbonate is recovered as an aqueous solution and recycled for use, and the hydrogen sulfide is removed from the exhaust gas. get to. The operation of this method requires a large amount of energy such as auxiliary fuel, fuel supply equipment, and air supply equipment, and the generated combustion gas contains a high concentration of hydrogen sulfide. It has disadvantages such as requiring
本発明の目的はチオシアン酸ナトリウム、チオ亜硫酸ナ
トリウム、硫酸ナトリウムを主として含有するコークス
炉ガス脱硫廃液の省エネルギー処理方法を提供すること
である
本発明の方法はチオシアン酸ナトリウム、チオ亜硫酸ナ
トリウム、硫酸ナトリウムを主成分とす形の硫酸ナトリ
ウム及び亜硫酸ガスを含むガスをいて実行する場合生成
する硫酸す) +7ウムにて流動層を形成しその流動層
中に直接原料廃液を噴霧することが可能である。反応条
件として炉内温度500℃以上であればチオシアン酸ナ
トリウムの分解反応は始まるが、650℃以上が最も高
分解率を示す、tた炉内温度800℃以上では生成し九
硫酸ナトリウムが溶融し流動状態に支障を来たす、従っ
て最も好ましい温度範囲は650〜700℃である。The purpose of the present invention is to provide an energy-saving treatment method for coke oven gas desulfurization waste liquid mainly containing sodium thiocyanate, sodium thiosulfite, and sodium sulfate. When carrying out the process using a gas containing sodium sulfate and sulfur dioxide gas as the main components, it is possible to form a fluidized bed at +7 um of sulfuric acid and spray the raw material waste directly into the fluidized bed. As for the reaction conditions, the decomposition reaction of sodium thiocyanate starts when the furnace temperature is 500°C or higher, but the highest decomposition rate is shown at 650°C or higher, and when the furnace temperature is 800°C or higher, sodium thiocyanate is formed and sodium thiocyanate is melted. The most preferred temperature range is therefore 650-700°C, which interferes with flow conditions.
本発明の方法を小型プラント例えば流動焙焼炉により研
究した結果、本濃縮脱硫廃液は粘性が高く流動層を形成
している硫酸ナトリウム粒子の成長を促進し比較的短時
間に流動状態の停止を来たすが、対生成硫酸ナトリウム
比25〜50X1粒度100〜150μの生成硫酸ナト
リウムを焙焼炉内にリサイクルすることと焙焼用空気の
場内流速を50〜60 ay’8 KすることKより長
期間安定した例えばソーダタカハックス法による脱硫廃
液の場合発熱物である硫黄化合物塩及びアルカリ炭酸塩
は2ON含有程度で操業するのが一般的であシ残り約8
0Xは水である。この2ON含有塩の発熱量は最も発熱
量の高いチオシアン酸ナトリウム上記両塩の含有率から
算出すると例として111処理するものとすれば−36
0−の吸熱側となシ、従って廃液中の水分を蒸発させ濃
縮する必要がある。As a result of research on the method of the present invention using a small plant such as a fluidized torrefaction furnace, it was found that this concentrated desulfurization waste liquid has a high viscosity and promotes the growth of sodium sulfate particles forming a fluidized bed, thereby stopping the fluidized state in a relatively short time. However, it is necessary to recycle the produced sodium sulfate with a particle size of 100 to 150μ to the produced sodium sulfate ratio of 25 to 50 x 1 into the roasting furnace, and to increase the in-house flow rate of the roasting air to 50 to 60 ay'8 K for a longer period of time than K. For example, in the case of a stable desulfurization waste liquid produced by the Soda Takahax method, the operation is generally carried out at a concentration of about 2ON in sulfur compound salts and alkali carbonates, which are exothermic substances, and the remaining amount is approximately 8.
0X is water. The calorific value of this 2ON-containing salt is calculated from the content of both sodium thiocyanate salts mentioned above, which has the highest calorific value.For example, if it is treated with 111, -36
It is on the endothermic side of 0-, therefore, it is necessary to evaporate and concentrate the water in the waste liquid.
濃縮度合については、熱経済性を考えて酸化焙焼用空気
と発生する高温の排ガスを熱交換することが得策であり
この熱交換率によって異なるが水分含有率約40〜60
%程度に濃縮することが必要・である。Regarding the degree of concentration, it is advisable to exchange heat between the oxidation and roasting air and the generated high-temperature exhaust gas in consideration of thermoeconomic efficiency, and the moisture content will vary depending on the heat exchange rate, but the moisture content will be approximately 40 to 60.
It is necessary to concentrate it to about %.
次に本発明の基本フローを図を用いて説明する。Next, the basic flow of the present invention will be explained using figures.
1の流動焙焼炉の流動層(波線部内)にA2インより供
給された脱硫濃縮廃液は反応条件として焙焼温度500
〜800℃、過剰空気率30〜SOS。The desulfurization concentrated waste liquid supplied from the A2 in to the fluidized bed (inside the broken line) of the fluidized roasting furnace No. 1 was heated to a roasting temperature of 500 as the reaction condition.
~800°C, excess air rate 30~SOS.
Bのオーツ々−70−ラインより第1ホツパー2へ抜き
出される。一方生成ガスは炉頂部より抜き出され、サイ
クロン3で同伴してくる微粒子硫酸ナトリウムを除去し
九後熱交換器4により空気fロワ6によって送られる焙
焼用空気と熱交換して脱硫廃液の濃縮度を低下せしめる
のに利用し系外へ出される。この生成ガスは、亜硫酸ガ
ス(80m)と適当な残存酸菓を含む丸めに硫酸製造用
原料ガスとして利用できる。一方加熱された焙焼用空気
は管路Eを経て、一部を濃縮廃液とリサイクル用硫酸ナ
トリウムの7トマイズ用として利用し残りは流動焙焼炉
の底部より炉内へ吹き込まれ流動層を形成する。サイク
ロン3で生成ガス中よυ除去された微粒子硫酸ナトリウ
ムは第2ホツパー5へ抜き出され、生成する硫酸ナトリ
ウムの25〜5ONtl−0ラインより再び焙焼炉内に
戻し残りはDラインよシ第1ホツノぞ−2に抜き出され
オー/セーフ0−ラインより抜き出される硫酸ナトリウ
ムと合流し製品として出荷する。The oats of B are extracted from the -70- line to the first hopper 2. On the other hand, the generated gas is extracted from the top of the furnace, and the entrained particulate sodium sulfate is removed by the cyclone 3. Afterwards, the generated gas is exchanged with the roasting air sent by the air f lower 6 by the heat exchanger 4, and the desulfurization waste liquid is removed. It is used to reduce the concentration and is discharged from the system. This generated gas can be used as a raw material gas for producing sulfuric acid, containing sulfur dioxide gas (80m) and appropriate residual acidity. On the other hand, the heated roasting air passes through pipe E, and part of it is used for totomizing concentrated waste liquid and sodium sulfate for recycling, and the rest is blown into the furnace from the bottom of the fluidized roasting furnace to form a fluidized bed. do. The particulate sodium sulfate removed from the generated gas by the cyclone 3 is taken out to the second hopper 5, and returned to the roasting furnace through the 25-5ONtl-0 line of the generated sodium sulfate, and the remainder is transferred to the D line and the second hopper. The sodium sulfate extracted from 1-Hotsunozo-2 is combined with the sodium sulfate extracted from O/Safe 0-line and shipped as a product.
次に本発明管実施例により説明する
内径30crIt@高さ3m・流動層1.5凰の試験用
焙焼炉を用いて硫酸ナトリウムを空気により流動層を形
成しておきその流動層内に第1表に示した様な組成の脱
硫濃縮廃液を噴霧する。Next, using a test roasting furnace with an inner diameter of 30 crIt @ 3 m height and a fluidized bed of 1.5 ㎜, sodium sulfate was formed with air to form a fluidized bed, and a fluidized bed was placed in the fluidized bed. A concentrated desulfurization waste liquid having the composition shown in Table 1 is sprayed.
次に反応条件の一例を第2表に示す
以上の様な条件下で第1表に示した廃液を酸化流−焙焼
した結果第3表に示す様な純度の硫酸ナトリウム及び第
4表に示す様な生成ガスを回収し九。Next, an example of the reaction conditions is shown in Table 2. Under the above conditions, the waste liquid shown in Table 1 was roasted in an oxidizing stream. 9. Collect the generated gas as shown.
第3表 第4表
本発明は、上述した如く構成し且つ用いることにより、
補助燃料を用いることなく、コークス炉ガス脱硫廃液の
処理を効率的に行なうことが出来る、省エネルギ処理方
法としてきわめて大きい効果を有する。Table 3 Table 4 By constructing and using the present invention as described above,
This method has an extremely large effect as an energy-saving treatment method that can efficiently treat coke oven gas desulfurization waste liquid without using auxiliary fuel.
第1図は、本発明方法を示す概略基本フローである。
1・・・流動焙焼炉 2・・・第+ホッノソー3・・
・サイクロン 4・・・熱3c洪器5・・・第二ホッ
ノ” 6 =−空f14. f cyヮ^・・・脱
硫濃縮廃液供給ライン
B・・・オーツセーフ0−ライン
C・・・焙焼炉へ戻しライン
D・・・第一ホツノぐ一抜出しライン
E・・・空気管路
代理人 弁理士 秋 沢 政 光
他°2名FIG. 1 is a schematic basic flow diagram illustrating the method of the present invention. 1...Fluidized roasting furnace 2...No. + Honnosaw 3...
・Cyclone 4...Heat 3c Hongki 5...Second Hokno" 6 =-Empty f14. Return line D to the furnace: First hot rod extraction line E: Air pipe agent, patent attorney, Masaaki Akizawa, and 2 other people
Claims (1)
ウム及び硫酸ナトリウムを含有するコークス炉ガス脱硫
廃液を七の壕\、若しくは濃縮の硫酸ナトリウムを回収
することを特徴とするコークス炉ガス脱硫廃液の処理方
法。(1) A method for treating coke oven gas desulfurization waste liquid, which comprises recovering coke oven gas desulfurization waste liquid containing sodium thiocyanate, sodium thiosulfite, and sodium sulfate into seven pits, or recovering concentrated sodium sulfate.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56169514A JPS5870876A (en) | 1981-10-23 | 1981-10-23 | Purifying treatment of desulfurizing waste liquid for coke oven gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56169514A JPS5870876A (en) | 1981-10-23 | 1981-10-23 | Purifying treatment of desulfurizing waste liquid for coke oven gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5870876A true JPS5870876A (en) | 1983-04-27 |
| JPS6345267B2 JPS6345267B2 (en) | 1988-09-08 |
Family
ID=15887913
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56169514A Granted JPS5870876A (en) | 1981-10-23 | 1981-10-23 | Purifying treatment of desulfurizing waste liquid for coke oven gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5870876A (en) |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS525313A (en) * | 1975-06-26 | 1977-01-17 | Toyobo Co Ltd | Method for opening continuous multifilament yarns |
-
1981
- 1981-10-23 JP JP56169514A patent/JPS5870876A/en active Granted
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS525313A (en) * | 1975-06-26 | 1977-01-17 | Toyobo Co Ltd | Method for opening continuous multifilament yarns |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6345267B2 (en) | 1988-09-08 |
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