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JPH0551524B2 - - Google Patents
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JPH0551524B2 - - Google Patents

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Publication number
JPH0551524B2
JPH0551524B2 JP334086A JP334086A JPH0551524B2 JP H0551524 B2 JPH0551524 B2 JP H0551524B2 JP 334086 A JP334086 A JP 334086A JP 334086 A JP334086 A JP 334086A JP H0551524 B2 JPH0551524 B2 JP H0551524B2
Authority
JP
Japan
Prior art keywords
alkali
reaction
gas
hydrogen sulfide
solution
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 - Fee Related
Application number
JP334086A
Other languages
Japanese (ja)
Other versions
JPS62162606A (en
Inventor
Yasuhiko Kamijo
Kazuhiro Mori
Yoshinobu Sato
Hajime Nakajima
Minoru Morita
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.)
Tsukishima Kikai Co Ltd
Original Assignee
Tsukishima Kikai Co Ltd
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 Tsukishima Kikai Co Ltd filed Critical Tsukishima Kikai Co Ltd
Priority to JP334086A priority Critical patent/JPS62162606A/en
Publication of JPS62162606A publication Critical patent/JPS62162606A/en
Publication of JPH0551524B2 publication Critical patent/JPH0551524B2/ja
Granted legal-status Critical Current

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  • Paper (AREA)

Description

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

〔産業上の利用分野〕 本発明はアルカリ硫黄化合物の熱分解処理方法
に関し、特に、硫化水素およびアルカリ分の回収
において従来技術を著しく改善する方法を提供す
る。 アルカリ硫黄化合物を分解して、アルカリ金属
を炭酸アルカリとして回収し、硫黄を硫化水素と
して回収する方法は、例えばパルプ蒸解液の処理
のように、有機物と結合した化合物を分離後、蒸
解薬品を回収する場合、或は乾式または温式排煙
脱硫装置から得られる亜硫酸ナトリウムや芒硝を
分解する場合等広く利用されている。回収される
炭酸アルカリ塩は脱硫工程に再循環され、一方、
発生する硫化水素は公知方法により単体硫黄およ
び硫酸製造に用いられ、あるいはMHD発電の際
に生じるシードの再生等に用いられる。また、硫
化水素を燃焼工程に送つて亜硫酸ガスとし、同時
に得られる炭酸アルカリ塩と反応させて、亜硫酸
アルカリ液としてパルプ蒸解用に再利用すること
もできる。 〔従来の技術〕 従来技術の1つとして、タンペラ法があり熱回
収ボイラーと組合せた中性亜硫酸パルプ
(NSSCP)蒸解液の回収法が知られている。この
タンペラ法は硫化ナトリウム、亜硫酸ナトリウム
を含む蒸解液を酸化燃焼させて硫化ナトリウムと
炭酸ナトリウムを得、これを水に溶解し、この溶
液を予備炭酸化してNaHSとNaHCO3を含む反
応液を製造する。この反応液を、Na2CO3とCO2
との別の反応工程で得られた固形の重炭酸ナトリ
ウムを反応させて、H2SとNa2CO3を生成させ
る。該H2Sは燃焼してSO2とし、これと前記工
程で得られるNa2CO3とを反応させて、亜硫酸塩
を得る方法である。 かかる従来法による硫化アルカリから炭酸アル
カリと硫化水素を得る主要な反応は、次の反応式
で表わすことができる。 (1) Na2S+CO2+H2O→NaHS+NaHCO3(炭
酸化塔) (2) NaHS+NaHCO3→Na2CO3+H2S(反応塔) (3) Na2CO3+CO2+H2O→2NaHCO3(重炭酸化
塔) また、SCAプロセスとして知られる還元分解
法がある。この方法の特徴は還元的雰囲気下にア
ルカリ硫黄化合物を700〜780℃で加熱して炭酸ア
ルカリと固形炭素(カーボン)および硫化水素に
分解し、次いでガス中から固形の炭酸アルカリを
分離し、溶解してカーボンを分離し、一方、硫化
水素をボイラーで燃焼してSO2を得、前記の炭酸
アルカリ水溶液と反応させて亜硫酸アルカリとし
て回収する方法である。 〔発明が解決しようとする問題点〕 一般に、タンペラ法のような反応形式は燃焼炉
を必要とし、また重曹の結晶を得るために複雑な
プロセスを要し大量の水蒸気を必要とすることか
ら、設備費が高くかつエネルギー的にも経済的で
ない。 また、SCA法では分解温度が比較的低いため、
供給物中のカーボンは全部分解せず、一部は固体
カーボンとして折出する。そのため炭酸アルカリ
との分離のためのロ過設備が必要であり、また得
られるカーボン燃焼のために新しい炉を必要とす
る。燃焼炉からの熱回収のためには複雑な操作の
廃熱ボイラーを取付ける必要も生じ、更にカーボ
ンの湿潤ケーキの水分は80%程度で、燃料として
用いるためには乾燥が必要である。このカーボン
を廃棄物として再利用しない場合には、パルプ蒸
解液中の貴重な有機物が燃料として有効に利用さ
れないばかりでなく、カーボンに付着したアルカ
リ、硫黄分が損失する。従つて、SCAプロセス
は設備コスト、エネルギーコストの面で非経済的
である。 〔問題点を解決するための手段〕 本発明は、前記従来技術の欠点をなくし、供給
液中の有機物質を完全に分解してカーボンを生成
させず、また有価薬剤の損失を最低限に抑制する
アルカリ硫黄化合物の熱分解処理方法を提供す
る。 本発明によれば、前記SCA法、あるいはタン
ペラ法と異なり、基本的には比較的高温の還元雰
囲気下でアルカリ硫黄化合物を熱分解させること
を特徴とする。即ち、本発明では、アルカリ硫黄
化合物を含む固形物、水溶液またはスラリーを還
元的雰囲気中で、800以上の温度で熱分解させる
ことが特徴である。これによつて原料中に含有さ
れる無機塩類はすべて溶融状態で炭酸塩化され、
カーボンを含む有機物は全てガス体として揮発さ
れ、硫黄は硫化水素に変換される。一方、炭酸塩
化された溶融物は硫化水素の存在による副反応で
生じた硫化アルカリを含むが、これは放散塔中
で、分解によつて生成したCO2および炭酸アルカ
リと反応して硫化アルカリは硫水素化アルカリ
に、炭酸アルカリの一部は重炭酸化アルカリに転
化される。放散塔内ではこれらは相互に反応して
H2Sを生成する。更に未反応分を含む反応液は
H2Sの分圧の低い二次放散塔内で加熱反応され、
これによつて、塔底から硫化アルカリを実質的に
含まない炭酸アルカリ溶液を、塔頂からは硫化水
素を回収する。 本発明によれば、分解を高温で行なうものであ
るから、カーボンのガス化により固体カーボンの
発生量が極めて少なく固体カーボンによるトラブ
ルを生じさせず、また反応液は純度が高く、環境
汚染、薬剤の損失のない方法が提供される。ま
た、反応工程中に炭酸アルカリを結晶で分離させ
る必要がなく、大量の蒸気を用いる蒸発工程もな
いので経済的にも有利である。 更に、Naの硫黄酸化物の熱分解処理に例とし
て本発明の反応経過を詳細に説明する。Naの硫
黄酸化物を反応炉中で高温還元雰囲気下に熱分解
する際、反応温度が高温になる程、酸化物の還元
が促進されるので、Na硫黄酸化物をほぼ完全に
炭酸ナトリウムと硫化水素に転換させるには、少
くとも800℃、好ましくは900〜1100℃の温度範囲
で処理することが必要である。 この条件下で生成するNa2CO3とH2Sを溶融状
態で瞬時に完全に分離させることは困難である。
本発明では、洗浄塔中において反応ガス全体を水
と接触させて炭酸ナトリウムの水溶液として分離
する。 この場合、最も困難な問題は、溶融物の主成分
である炭酸ナトリウムと反応生成物の硫化水素と
が反応器中で逆反応してNa2Sを生成させること
である。このような反応によつてNa2Sが生成す
ると、生成する炭酸ナトリウム溶液にNa2Sが存
在して、例えばパルプ蒸解に再利用する際に硫化
水素が発生し、また、反応の点からも分解が低下
するので、アルカリを再利用する場合の循環量が
多くなり経済的ではない。さらに、本発明方法に
よつて得られる硫化水素を燃焼して亜硫酸ガスと
し、これを炭酸ナトリウムと接触させて亜硫酸ナ
トリウムを得る際にも、Na2Sを含む炭酸ナトリ
ウム水溶液を使用すると、SO2の吸収につれて
H2Sが放出される。これは薬品の回収率の減少
と大気汚染の問題を生じさせる。 このような逆反応、Na2CO3+H2S→Na2S、
は操作上避けられないので、本発明では、接触式
洗浄塔で得られる液を炭酸ガスを含む洗浄塔排ガ
スと多段向流的に接触させて次の反応を行なわせ
るのである。 H2S+(Na2S+CO2+Na2CO3+H2O)
〓NaHS+NaHCO3+H2S↑ (1) この反応は本発明では常圧下、またガス相には
硫化水素が存在するところで行なわれる。したが
つて、通常、右辺から左辺に反応が移動する条件
は満されず、反応は右辺に進む。 この反応生成物の水溶液を多段向流塔の底部か
ら取り出し、硫化水素の分圧の低い二次放散塔中
で加熱下に反応を行なわせると、次式の反応が進
行する。 NaHS+NaHCO3→ Na2CO3+H2S↑ (2) この反応には真空下で僅かの水蒸気の存在で行
なうのが適当である。 本発明方法は分解ガス中の炭酸ガスを有効に利
用するので、タンペラ法と異なり、別のガス源を
必要としない。一方、反応液中のNaHSと
NaHCO3によつてH2S分圧の低い条件下で反応
させるので、固形物として重炭酸ナトリウムを循
環使用する必要もなく、設備費および用液費共、
著しく経済的である。 第1図は本発明方法を実施するためのフローシ
ートの一例である。反応塔1には原料供給ライン
11と空気供給ライン12があり、ここで高温還
元分解が行なわれる。反応生成物は洗浄塔2に送
られ、そこでライン13からの水と接触される。
洗浄水によつて反応生成物は溶解され、得られた
水溶液はライン14を経て一次放散塔3の塔頂部
に供給され、底部からは洗浄塔2の塔頂からライ
ン15を経て送られる洗浄済ガスを供給して向流
的に接触させる。一次放散塔では前記式(1)の反応
が十分に達成しうるように数段の多孔層を設ける
のが好ましい。かくして、一次放散塔の頂部から
は比較的純粋な形でライン17を経てH2Sが取
出される。反応液はライン16を経て多段式二次
放散塔4の塔頂部分に供給される。二次放散塔4
の塔頂部にはコンデンサー5を介して真空ポンプ
6が装着されており、該放散塔内における前記式
(2)の反応がH2S分圧の低い状態(80〜85℃、300
〜400mmHg)で行われ、かつ塔底部にはスチーム
のような加熱媒体24が導入されて、液が塔内を
下降中に前記反応が十分完了するように考慮され
ている。この反応で生成するH2Sガスは吸引さ
れてコンデンサー5により冷却され、水分が除去
された形でライン20を経て、一次放散塔の頂部
からのH2Sガスと合体される。一方、二次放散
塔の底部から取出される反応液は反応によつて生
成された炭酸ナトリウムを主成分とする水溶液で
ある。 本発明方法の基本はH2Sと発生させる工程が
主体であるが、分離された各塔からのH2Sは燃
焼炉7に送り、25から空気を導入して燃焼さ
せ、この燃焼ガスをSO2吸収塔8に送り、二次放
散塔から流出する炭酸ナトリウム溶液と接触させ
れば、亜硫酸ナトリウムとしてアルカリを回収す
ることができる。また、回収されたH2Sはその
他単体硫黄製造等に利用することができる。 更に、本発明の方法を熱回収の面から反応炉の
後に、第2図に示すように、廃熱ボイラーを併置
させることもできる。第2図で31は廃熱ボイラ
ー、30は溶融物受槽である。この受槽に溶解水
を加え、ここで新しい溶解液を作り、高温ガスは
廃熱ボイラーに通じて熱回収した後、前記一次放
散塔下部に供給し、溶解液を一次放散塔の頂部へ
供給して熱回収が行なわれる。また、第3図のよ
うに、反応ガスを冷却塔41に送り、高温ガスを
得て、これを蒸発缶43の熱交換器42に送つ
て、脱湿の際の凝縮液で被蒸発液に熱を与え、放
散塔3への溶液の濃縮をも行なわせることもでき
る。更に、燃焼炉7をガス炊きボイラーとして蒸
気を回収することも可能である。 〔実施例〕 供給原料として中性亜硫酸パルプ蒸解液を用
い、第1図に示す装置を使用して本発明の高温還
元分解法を行なつた。原液の濃縮組成は次の通り
である。 液 濃 度 55重量% 組成 Na 13.0重量% S 8.8 〃 C 30.3 〃 H 3.2 〃 O 45.0 〃 Na2SO4 10.0 〃 発熱量 3000Kcal/Kg 反応塔は直径4.4m、高さ4.5mである。上記凝
縮原料を反応塔の頂部から6000Kg/Hの割合で供
給し、空気量を9400Nm3/Hとして、反応過度を
900℃として反応させた。 かくして得られたガスと溶融物を洗浄塔内で洗
浄液と接触させる。洗浄塔から得られた水溶液の
組成は次の通りであつた。 Na2CO3 57.8重量% Na2S 35.3 〃 Na2SO4 6.8 〃 この水溶液を直径2.7m、高さ12mで、6段の
多孔板を有する一次放散塔の塔頂部に供給し、下
部に洗浄塔からのガスを供給する。一次放散塔で
は前記式(1)の反応が進行し、次表の組成(乾物
量)を有する溶液が得られた。 Na2CO3 80.7重量% Na2S 11.7 〃 Na2SO4 7.6 〃 次に、得られた水溶液を、直径12m、高さ
4.5mで、10段の多孔板を有する二次放散塔の頂
部に供給した。二次放散塔の底部からは600〜800
Kg/Hのスチームが供給されて、ここで式(2)の、
反応が完結される。得られた塔底液の組成(乾物
換算)は次の通りであつた。 Na2CO3 92.0重量% Na2S 1.5 〃 Na2SO4 6.5 〃 前記一次放散塔からのガスの組成は容量%で表
わして、CO2 14.9%、CO 1.4%、H2 8.8%、
H2S 1.6%、CH4 0.1%、N2 58.1%、H2
12.1%であり、流出量は13000Nm3/Hであつた。 上記のようにして得られた炭酸ナトリウム溶液
はNa2S含量が少なく、また吸収工程に送つたと
きにも硫化ナトリウムの存在によるSO2吸収工程
のトラブルや生成亜硫酸塩をパルプ蒸解に使用し
たときにも悪臭の問題を生ぜず、従来技術の問題
点がすべて解決されることが判つた。 〔発明の効果〕 本発明の方法による効果を、廃熱ボイラーおよ
びガス炊きボイラー設置した場合に、
NSSCP200T/Dプラントで、従来技術のSCA法
と比較したときの結果で示すと、次のようであ
る。
[Industrial Field of Application] The present invention relates to a method for thermal decomposition of alkali sulfur compounds, and in particular provides a method that significantly improves the prior art in the recovery of hydrogen sulfide and alkali components. The method of decomposing alkali sulfur compounds, recovering alkali metals as alkali carbonates, and recovering sulfur as hydrogen sulfide involves separating compounds combined with organic matter and recovering cooking chemicals, such as in the treatment of pulp cooking liquor. It is widely used to decompose sodium sulfite and mirabilite obtained from dry or hot flue gas desulfurization equipment. The recovered alkali carbonates are recycled to the desulfurization process, while
The generated hydrogen sulfide is used to produce elemental sulfur and sulfuric acid by known methods, or used to regenerate seeds generated during MHD power generation. Alternatively, hydrogen sulfide can be sent to a combustion process to produce sulfur dioxide gas, and simultaneously reacted with the resulting alkali carbonate to be reused as an alkaline sulfite solution for pulp cooking. [Prior Art] One of the conventional technologies is the Tampera method, which is a known method for recovering neutral sulfite pulp (NSSCP) cooking liquor in combination with a heat recovery boiler. This Tampera method oxidizes and burns cooking liquor containing sodium sulfide and sodium sulfite to obtain sodium sulfide and sodium carbonate, which are dissolved in water and pre-carbonated to produce a reaction solution containing NaHS and NaHCO3 . do. This reaction solution was mixed with Na 2 CO 3 and CO 2
The solid sodium bicarbonate obtained in a separate reaction step is reacted with H 2 S and Na 2 CO 3 to produce H 2 S and Na 2 CO 3 . The H 2 S is burned to form SO 2 and this is reacted with Na 2 CO 3 obtained in the above step to obtain sulfite. The main reaction for obtaining alkali carbonate and hydrogen sulfide from alkali sulfide according to the conventional method can be expressed by the following reaction formula. (1) Na 2 S + CO 2 + H 2 O → NaHS + NaHCO 3 (carbonation tower) (2) NaHS + NaHCO 3 → Na 2 CO 3 + H 2 S (reaction tower) (3) Na 2 CO 3 + CO 2 + H 2 O → 2NaHCO 3 (Bicarbonation tower) There is also a reductive decomposition method known as the SCA process. The characteristics of this method are that an alkali sulfur compound is heated at 700 to 780°C in a reducing atmosphere to decompose it into alkali carbonate, solid carbon, and hydrogen sulfide, and then the solid alkali carbonate is separated from the gas and dissolved. In this method, hydrogen sulfide is burned in a boiler to obtain SO 2 , which is then reacted with the aqueous alkali carbonate solution and recovered as alkali sulfite. [Problems to be solved by the invention] In general, a reaction method such as the Tampera method requires a combustion furnace, and also requires a complicated process and a large amount of steam to obtain crystals of baking soda. Equipment costs are high and it is not economical in terms of energy. In addition, since the decomposition temperature is relatively low in the SCA method,
All of the carbon in the feed is not decomposed, and some of it is precipitated as solid carbon. Therefore, filtration equipment is required for separation from the alkali carbonate, and a new furnace is required for combustion of the resulting carbon. In order to recover heat from the combustion furnace, it is necessary to install a waste heat boiler with complicated operation, and the wet cake of carbon has a moisture content of about 80% and must be dried before it can be used as a fuel. If this carbon is not reused as waste, not only will the valuable organic matter in the pulp cooking liquor not be used effectively as fuel, but also the alkali and sulfur content attached to the carbon will be lost. Therefore, the SCA process is uneconomical in terms of equipment costs and energy costs. [Means for Solving the Problems] The present invention eliminates the drawbacks of the prior art, completely decomposes organic substances in the feed liquid, does not generate carbon, and minimizes the loss of valuable chemicals. The present invention provides a method for thermally decomposing an alkali sulfur compound. According to the present invention, unlike the SCA method or Tampera method, the alkali sulfur compound is basically thermally decomposed in a reducing atmosphere at a relatively high temperature. That is, the present invention is characterized in that a solid material, aqueous solution, or slurry containing an alkali sulfur compound is thermally decomposed at a temperature of 800° C. or higher in a reducing atmosphere. As a result, all the inorganic salts contained in the raw materials are carbonated in the molten state,
All organic matter, including carbon, is volatilized as a gas, and sulfur is converted to hydrogen sulfide. On the other hand, the carbonated melt contains alkali sulfide produced by a side reaction due to the presence of hydrogen sulfide, which reacts with CO 2 and alkali carbonate produced by decomposition in the stripping tower to form alkali sulfide. A portion of the alkali carbonate is converted to alkali bicarbonate into alkali sulfide. Inside the emission tower, these react with each other.
Generate H 2 S. Furthermore, the reaction solution containing unreacted components is
A heating reaction is carried out in a secondary stripping tower with a low partial pressure of H 2 S,
As a result, an alkaline carbonate solution substantially free of alkali sulfide is recovered from the bottom of the column, and hydrogen sulfide is recovered from the top of the column. According to the present invention, since the decomposition is carried out at high temperatures, the amount of solid carbon generated by gasification of carbon is extremely small, and troubles caused by solid carbon do not occur, and the reaction liquid is of high purity and is free from environmental pollution and pharmaceutical agents. A lossless method is provided. Furthermore, it is economically advantageous since there is no need to separate the alkali carbonate into crystals during the reaction process, and there is no evaporation process that uses a large amount of steam. Furthermore, the reaction process of the present invention will be explained in detail by taking as an example the thermal decomposition treatment of sulfur oxide of Na. When sulfur oxides of Na are thermally decomposed in a high-temperature reducing atmosphere in a reactor, the higher the reaction temperature, the faster the reduction of the oxides, so the sulfur oxides of Na are almost completely converted into sodium carbonate and sulfurized. Conversion to hydrogen requires treatment at a temperature range of at least 800°C, preferably 900-1100°C. It is difficult to instantly and completely separate Na 2 CO 3 and H 2 S produced under these conditions in a molten state.
In the present invention, the entire reaction gas is brought into contact with water in a washing tower and separated as an aqueous solution of sodium carbonate. In this case, the most difficult problem is that the main component of the melt, sodium carbonate, and the reaction product, hydrogen sulfide, react back in the reactor to form Na 2 S. When Na 2 S is generated by such a reaction, Na 2 S is present in the resulting sodium carbonate solution, and hydrogen sulfide is generated when the sodium carbonate solution is reused, for example, for pulp cooking. Since decomposition is reduced, the amount of circulation when reusing alkali increases, which is not economical. Furthermore, when hydrogen sulfide obtained by the method of the present invention is burned to produce sulfur dioxide gas and this is brought into contact with sodium carbonate to obtain sodium sulfite, if an aqueous sodium carbonate solution containing Na 2 S is used, SO 2 as the absorption of
H 2 S is released. This results in reduced drug recovery and air pollution problems. Such a reverse reaction, Na 2 CO 3 + H 2 S → Na 2 S,
Since this is unavoidable in operation, in the present invention, the liquid obtained in the contact type washing tower is brought into contact with the washing tower exhaust gas containing carbon dioxide gas in a multistage countercurrent manner to carry out the following reaction. H 2 S+ (Na 2 S + CO 2 + Na 2 CO 3 + H 2 O)
〓NaHS+NaHCO 3 +H 2 S↑ (1) In the present invention, this reaction is carried out under normal pressure and in the presence of hydrogen sulfide in the gas phase. Therefore, the conditions for the reaction to move from the right-hand side to the left-hand side are usually not satisfied, and the reaction proceeds to the right-hand side. When the aqueous solution of the reaction product is taken out from the bottom of the multistage countercurrent tower and reacted under heating in a secondary stripping tower where the partial pressure of hydrogen sulfide is low, the reaction of the following formula proceeds. NaHS + NaHCO 3 → Na 2 CO 3 + H 2 S↑ (2) This reaction is suitably carried out under vacuum and in the presence of a small amount of water vapor. Since the method of the present invention effectively utilizes carbon dioxide gas in the cracked gas, unlike the Tampera method, no separate gas source is required. On the other hand, NaHS in the reaction solution
Since the reaction is carried out using NaHCO 3 under conditions of low H 2 S partial pressure, there is no need to recycle sodium bicarbonate as a solid substance, and equipment costs and liquid costs are reduced.
It is extremely economical. FIG. 1 is an example of a flow sheet for carrying out the method of the present invention. The reaction tower 1 has a raw material supply line 11 and an air supply line 12, in which high-temperature reductive decomposition is performed. The reaction product is sent to washing column 2 where it is contacted with water from line 13.
The reaction product is dissolved by the washing water, and the resulting aqueous solution is supplied to the top of the primary stripping tower 3 via line 14, and from the bottom, the washed solution is sent from the top of the washing tower 2 via line 15. Gas is supplied and brought into contact in a countercurrent manner. In the primary stripping tower, it is preferable to provide several porous layers so that the reaction of formula (1) can be sufficiently achieved. H 2 S is thus removed from the top of the primary stripper via line 17 in relatively pure form. The reaction liquid is supplied to the top portion of the multi-stage secondary stripping tower 4 via a line 16. Secondary emission tower 4
A vacuum pump 6 is installed at the top of the column via a condenser 5, and the above formula in the stripping column is
The reaction (2) is carried out under conditions of low H 2 S partial pressure (80-85℃, 300℃
~400 mmHg), and a heating medium 24 such as steam is introduced at the bottom of the column to ensure that the reaction is sufficiently completed while the liquid is descending within the column. The H 2 S gas produced in this reaction is drawn in and cooled by a condenser 5, and in a dehydrated form passes through a line 20 and is combined with the H 2 S gas from the top of the primary stripping tower. On the other hand, the reaction liquid taken out from the bottom of the secondary stripping tower is an aqueous solution whose main component is sodium carbonate produced by the reaction. The basis of the method of the present invention is mainly the process of generating H 2 S, but the H 2 S from each separated column is sent to the combustion furnace 7, air is introduced from 25 and combusted, and this combustion gas is If it is sent to the SO 2 absorption tower 8 and brought into contact with the sodium carbonate solution flowing out from the secondary stripping tower, the alkali can be recovered as sodium sulfite. In addition, the recovered H 2 S can be used for other purposes such as producing elemental sulfur. Furthermore, in the method of the present invention, a waste heat boiler can be placed in parallel with the reactor, as shown in FIG. 2, from the viewpoint of heat recovery. In FIG. 2, 31 is a waste heat boiler, and 30 is a melt receiving tank. Dissolved water is added to this receiver tank to create a new dissolved solution, and the high-temperature gas is passed through a waste heat boiler to recover heat, then supplied to the lower part of the primary stripping tower, and the dissolved solution is supplied to the top of the primary stripping tower. Heat recovery is performed. In addition, as shown in FIG. 3, the reaction gas is sent to the cooling tower 41 to obtain high-temperature gas, which is sent to the heat exchanger 42 of the evaporator 43 and converted into the liquid to be evaporated with the condensate during dehumidification. Heat can also be applied to cause the solution to be concentrated in the stripping tower 3. Furthermore, it is also possible to recover steam by using the combustion furnace 7 as a gas-fired boiler. [Example] Using neutral sulfite pulp cooking liquor as a feedstock, the high temperature reductive decomposition method of the present invention was carried out using the apparatus shown in FIG. The concentrated composition of the stock solution is as follows. Liquid Concentration 55% by weight Composition Na 13.0% by weight S 8.8 C 30.3 H 3.2 O 45.0 Na 2 SO 4 10.0 Calorific value 3000 Kcal/Kg The reaction tower has a diameter of 4.4 m and a height of 4.5 m. The above condensed raw material was supplied from the top of the reaction tower at a rate of 6000 Kg/H, and the amount of air was set to 9400 Nm 3 /H to prevent excessive reaction.
The reaction was carried out at 900°C. The gas and melt thus obtained are brought into contact with a cleaning liquid in a cleaning column. The composition of the aqueous solution obtained from the washing tower was as follows. Na 2 CO 3 57.8% by weight Na 2 S 35.3 〃 Na 2 SO 4 6.8 〃 This aqueous solution is supplied to the top of the primary stripping tower, which has a diameter of 2.7 m and a height of 12 m and has six perforated plates, and is washed at the bottom. Supply gas from the tower. In the primary stripping tower, the reaction of formula (1) proceeded, and a solution having the composition (dry weight) shown in the table below was obtained. Na 2 CO 3 80.7% by weight Na 2 S 11.7 〃 Na 2 SO 4 7.6 〃 Next, the obtained aqueous solution was placed in a container with a diameter of 12 m and a height of
4.5 m and fed to the top of a secondary stripping tower with 10 stages of perforated plates. 600-800 from the bottom of the secondary emission tower
Kg/H of steam is supplied, where equation (2),
The reaction is completed. The composition of the bottom liquid obtained (in terms of dry matter) was as follows. Na 2 CO 3 92.0% by weight Na 2 S 1.5 〃 Na 2 SO 4 6.5 〃 The composition of the gas from the primary stripping tower is expressed in volume %: CO 2 14.9%, CO 1.4%, H 2 8.8%,
H2S 1.6%, CH4 0.1%, N2 58.1%, H2O
It was 12.1%, and the outflow amount was 13000Nm 3 /H. The sodium carbonate solution obtained as described above has a low Na 2 S content, and when sent to the absorption process, there are problems with the SO 2 absorption process due to the presence of sodium sulfide and when the produced sulfite is used for pulp cooking. It has been found that all the problems of the prior art are solved without causing any odor problems. [Effects of the invention] The effects of the method of the invention can be obtained when a waste heat boiler and a gas boiler are installed.
The results of a comparison with the conventional SCA method in the NSSCP200T/D plant are as follows.

【表】 以上の様に、本発明方法の経済的優位が判明し
た。また、上表での動力消費量の減少は、主に本
発明方法ではカーボンの発生が殆んどないので、
ロ過設備を要しないためである。更に、本発明方
法の利点として、回収液中の芒硝の量が少ないこ
とが挙げられる。これは本発明の反応方法によれ
ば、供給液中の芒硝が殆んど分解して炭酸ナトリ
ウムとなり、回収薬液中の芒硝量は極めて少な
い。このため、黒液の濃縮工程において芒硝の折
出による蒸発操作上のトラブルがなく、最終濃度
を従来法に較べて高くすることができる。
[Table] As described above, the economical advantage of the method of the present invention has been revealed. In addition, the reduction in power consumption in the table above is mainly due to the fact that almost no carbon is generated in the method of the present invention.
This is because no filtration equipment is required. Furthermore, an advantage of the method of the present invention is that the amount of Glauber's salt in the recovered liquid is small. This is because, according to the reaction method of the present invention, most of the mirabilite in the feed liquid is decomposed into sodium carbonate, and the amount of mirabilite in the recovered chemical solution is extremely small. Therefore, there is no trouble in the evaporation operation due to precipitation of Glauber's salt in the black liquor concentration process, and the final concentration can be made higher than in the conventional method.

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

第1図は本発明を実施するための装置構成を示
すフローシートの一例である。第2図は熱回収の
ための廃熱ボイラーを併置する場合のフローシー
トの一部である。第3図は熱回収を伴なう他のフ
ローシートの一部である。 1……反応塔、2……洗浄塔、3……一次放散
塔、4……二次放散塔、5……コンデンサー、6
……真空ポンプ、7……燃焼炉、8……SO2吸収
塔、30……溶融物受槽、31……廃熱ボイラ
ー、41……冷却塔、42……熱交換器、43…
…蒸発缶、44……コンデンサー。
FIG. 1 is an example of a flow sheet showing the configuration of an apparatus for implementing the present invention. Figure 2 is a part of a flow sheet when a waste heat boiler is installed for heat recovery. FIG. 3 is part of another flow sheet involving heat recovery. 1... Reaction tower, 2... Washing tower, 3... Primary stripping tower, 4... Secondary stripping tower, 5... Condenser, 6
... Vacuum pump, 7 ... Combustion furnace, 8 ... SO 2 absorption tower, 30 ... Melt receiving tank, 31 ... Waste heat boiler, 41 ... Cooling tower, 42 ... Heat exchanger, 43 ...
...Evaporator, 44...Condenser.

Claims (1)

【特許請求の範囲】 1 アルカリ硫黄化合物を含む固形物、水溶液ま
たはスラリーを還元的雰囲気中で800℃以上の温
度で熱分解し、生成する溶融物を水に溶解し、生
成する水溶液と前記熱分解で発生した炭酸ガスを
含むガス流とを接触させ、溶液中の硫化アルカリ
を硫化水素アルカリに、炭酸アルカリの一部を重
炭酸アルカリに転化させると共に、これらをH2
S分圧の低減された条件下に相互に反応させて、
生成する硫化水素ガスと炭酸アルカリ溶液とを回
収することを特徴とするアルカリ硫黄化合物の熱
分解処理方法。 2 前記の回収された硫化水素を燃焼して亜硫酸
ガスの形とし、これを前記回収した炭酸アルカリ
溶液と反応させ、得られる亜硫酸アルカリを回収
する工程を更に含む特許請求の範囲第1項記載の
方法。
[Claims] 1. A solid substance, aqueous solution or slurry containing an alkali sulfur compound is thermally decomposed at a temperature of 800°C or higher in a reducing atmosphere, the resulting melt is dissolved in water, and the resulting aqueous solution and the heat The alkali sulfide in the solution is converted into alkali hydrogen sulfide and a portion of the alkali carbonate into alkali bicarbonate by contacting the gas stream containing carbon dioxide gas generated during decomposition, and these are converted into H 2
Reacting with each other under conditions of reduced S partial pressure,
A method for thermally decomposing an alkali sulfur compound, which comprises recovering generated hydrogen sulfide gas and an alkali carbonate solution. 2. The method according to claim 1, further comprising the step of burning the recovered hydrogen sulfide to form sulfur dioxide gas, reacting it with the recovered alkali carbonate solution, and recovering the resulting alkali sulfite. Method.
JP334086A 1986-01-10 1986-01-10 Method for thermal decomposition treatment of alkali sulfur compound Granted JPS62162606A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP334086A JPS62162606A (en) 1986-01-10 1986-01-10 Method for thermal decomposition treatment of alkali sulfur compound

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP334086A JPS62162606A (en) 1986-01-10 1986-01-10 Method for thermal decomposition treatment of alkali sulfur compound

Publications (2)

Publication Number Publication Date
JPS62162606A JPS62162606A (en) 1987-07-18
JPH0551524B2 true JPH0551524B2 (en) 1993-08-02

Family

ID=11554625

Family Applications (1)

Application Number Title Priority Date Filing Date
JP334086A Granted JPS62162606A (en) 1986-01-10 1986-01-10 Method for thermal decomposition treatment of alkali sulfur compound

Country Status (1)

Country Link
JP (1) JPS62162606A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2676927A1 (en) * 2012-06-22 2013-12-25 Evonik Industries AG Method and reactor for producing hydrogen sulphide
CN103693780A (en) * 2013-12-20 2014-04-02 四川省洪雅青衣江元明粉有限公司 Method and device for nitrified water purification used for comprehensive utilization of energy conservation and emission reduction
CN116425121B (en) * 2023-05-22 2024-07-05 南风化工(运城)集团有限公司 Sodium sulfide production method

Also Published As

Publication number Publication date
JPS62162606A (en) 1987-07-18

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