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JPS5943600B2 - Improved methods for chemical recovery in paper mills - Google Patents
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JPS5943600B2 - Improved methods for chemical recovery in paper mills - Google Patents

Improved methods for chemical recovery in paper mills

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Publication number
JPS5943600B2
JPS5943600B2 JP51121286A JP12128676A JPS5943600B2 JP S5943600 B2 JPS5943600 B2 JP S5943600B2 JP 51121286 A JP51121286 A JP 51121286A JP 12128676 A JP12128676 A JP 12128676A JP S5943600 B2 JPS5943600 B2 JP S5943600B2
Authority
JP
Japan
Prior art keywords
liquid
absorption
hydrogen sulfide
liquor
dioxide 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.)
Expired
Application number
JP51121286A
Other languages
Japanese (ja)
Other versions
JPS5349102A (en
Inventor
広二 桝野
純司 中山
充良 金子
行生 溝口
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP51121286A priority Critical patent/JPS5943600B2/en
Publication of JPS5349102A publication Critical patent/JPS5349102A/en
Publication of JPS5943600B2 publication Critical patent/JPS5943600B2/en
Expired legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Paper (AREA)

Description

【発明の詳細な説明】 従来、ガス中の硫化水素を吸収するためには、pH10
以上のアルカリ水溶液が用いられる。
[Detailed Description of the Invention] Conventionally, in order to absorb hydrogen sulfide in gas, the pH is 10.
The above alkaline aqueous solutions are used.

そして、この液を硫化水素吸収に用いることは当然者え
られ、吸収効果も充分であることは明らかである。
It is obvious that this liquid can be used to absorb hydrogen sulfide, and it is clear that the absorption effect is sufficient.

しかし、硫化水素吸収液として循環使用すると液中に硫
化物が蓄積され、次第に硫化水素吸収効果が落ちてくる
However, when used repeatedly as a hydrogen sulfide absorption liquid, sulfide accumulates in the liquid, and the hydrogen sulfide absorption effect gradually decreases.

したがって継続して硫化水素の吸収効果を保たせるため
には、何らかの方法で液中の硫化物を除く必要がある。
Therefore, in order to continue to maintain the hydrogen sulfide absorption effect, it is necessary to remove sulfide from the liquid by some method.

その方法として、硫化物を空気酸化させて液中の硫化物
濃度を下げることが考えられるが、それには当然大きな
酸化設備が必要となる。
One possible method for this is to reduce the sulfide concentration in the liquid by oxidizing the sulfide in the air, but this naturally requires large oxidation equipment.

さらに、pH10以上のアルカリ液を使う場合には、排
ガス中に含まれる相当量の炭酸ガスがアルカリを消費し
、経済的にも好ましくない。
Furthermore, when using an alkaline solution with a pH of 10 or more, a considerable amount of carbon dioxide gas contained in the exhaust gas consumes the alkali, which is not economically preferable.

pH9以下であれば、炭酸ガスを吸収することはないが
、硫化水素の吸収は50〜40%以下となってしまう。
If the pH is 9 or less, carbon dioxide gas will not be absorbed, but hydrogen sulfide absorption will be 50 to 40% or less.

しかし、本方法では、微量の硫酸鉄、硫酸ニッケル、硫
酸マンガン、等の鉄塩、ニッケル塩、マンガン塩、の各
塩類を単独に、又は上記の各塩類を2種以上混合して触
媒として添加するだけで、大きな酸化設備を必要とせず
、しかもpH10以下の領域で、炭酸ガスの影響を受け
ずに、選択的に硫化水素及び亜硫酸ガスを吸収すること
ができる。
However, in this method, trace amounts of iron salts, nickel salts, manganese salts such as iron sulfate, nickel sulfate, manganese sulfate, etc. are added as a catalyst either singly or in a mixture of two or more of the above salts. By simply doing this, it is possible to selectively absorb hydrogen sulfide and sulfur dioxide gas without the need for large oxidation equipment and in a pH range of 10 or less without being affected by carbon dioxide gas.

さらに、硫化水素、亜硫酸ガスの吸収により消費された
アルカリを補給するアルカリ液として、製紙工場薬品回
収工程で生じる薬液を使用することを特徴とするもので
ある。
Furthermore, the present invention is characterized in that a chemical solution generated in the paper mill chemical recovery process is used as an alkaline solution to replenish the alkali consumed by absorption of hydrogen sulfide and sulfur dioxide gas.

吸収液として用いるアルカリ性水溶液はpHの高い領域
では炭酸ガスを吸収し、そのため、pH値が下がるが、
やがてガス中の炭酸ガス分圧と平衡の液組成になるとそ
れ以上の炭酸ガスの吸収は起こらず、炭酸ガスによるp
Hの低下はみられなくなる。
The alkaline aqueous solution used as the absorbing liquid absorbs carbon dioxide gas in a high pH region, and as a result, the pH value decreases.
Eventually, when the liquid composition reaches equilibrium with the partial pressure of carbon dioxide in the gas, no further absorption of carbon dioxide occurs, and the p due to carbon dioxide gas increases.
No decrease in H is observed.

このpH低下の停止傾向はpH10以下から始まり、p
H9前後で落ち着く。
This tendency for pH to stop decreasing begins at pH 10 or lower, and p
It will settle down around H9.

また、pH値8,3以下になると、液中より炭酸ガスが
発生し始める。
Further, when the pH value becomes 8.3 or less, carbon dioxide gas starts to be generated from the liquid.

したがって、硫化水素及び亜硫酸ガスを吸収除去する吸
収液としてアルカリ性水溶液を用いる場合のpH領域は
8.3〜pH1,0,0とするのが望ましい。
Therefore, when using an alkaline aqueous solution as an absorbing liquid for absorbing and removing hydrogen sulfide and sulfur dioxide gas, the pH range is preferably 8.3 to pH 1.0.0.

また、吸収液濃度は高い程硫化水素及び亜硫酸ガスの吸
収効果が良いが、炭酸ナトリウム換算として2重量%以
上で吸収効果があった。
Furthermore, the higher the concentration of the absorption liquid, the better the absorption effect of hydrogen sulfide and sulfur dioxide gas, but the absorption effect was found at 2% by weight or more in terms of sodium carbonate.

さらに、吸収液温度は20℃〜95℃で、硫化水素及び
亜硫酸ガスの吸収効果がよかった。
Furthermore, the absorption liquid temperature was 20°C to 95°C, and the absorption effect of hydrogen sulfide and sulfur dioxide gas was good.

以上のpH1濃度、温度条件下で前記触媒の添加により
、硫化水素及び亜硫酸ガスの高い吸収効果を得た。
By adding the catalyst under the above pH 1 concentration and temperature conditions, a high effect of absorbing hydrogen sulfide and sulfur dioxide gas was obtained.

触媒としての各種金属塩は微量で良(,307n9/l
以下でも充分な吸収効果を発揮する。
Various metal salts as catalysts can be used in small amounts (307n9/l)
Sufficient absorption effect can be achieved even below.

鉄塩、マンガン塩、ニッケル塩、としては、硫酸鉄、塩
化鉄、硝酸鉄、水酸化鉄、炭酸鉄、リン酸鉄、酢酸鉄、
硫酸鉄アンモニウム、鉄キレート化合物及び硫酸マンガ
ン、塩化マンガン、硝酸マンガン、水酸化マンガン、炭
酸マンガン、リン酸マンガン及び硫酸ニッケル、塩化ニ
ッケル、硝酸ニッケル、水酸化ニッケル、炭酸ニッケル
、リン酸ニッケル、酢酸ニッケル等の鉄、マンガン、ニ
ッケル、の各化合物を使用することができる。
Iron salts, manganese salts, nickel salts include iron sulfate, iron chloride, iron nitrate, iron hydroxide, iron carbonate, iron phosphate, iron acetate,
Ammonium iron sulfate, iron chelate compounds and manganese sulfate, manganese chloride, manganese nitrate, manganese hydroxide, manganese carbonate, manganese phosphate and nickel sulfate, nickel chloride, nickel nitrate, nickel hydroxide, nickel carbonate, nickel phosphate, nickel acetate Compounds of iron, manganese, nickel, etc. can be used.

本発明は、以上の諸条件下で硫化水素及び亜硫酸ガスを
効率よく吸収する際に、硫化水素及び亜硫酸ガスの吸収
により消費されたアルカリの補給用アルカリとして、製
紙工場の薬品回収工程中に生ずるアルカリ水溶液例えば
緑液または白液もしくは弱液等の薬液を使用し、回収ボ
イラー等の製紙工場薬品回収工程中に生じる排ガス中に
逃げる硫化水素、亜硫酸ガスを吸収し、吸収した液は1
部抜き出して薬品回収工程に戻し、該イオウ分を有効に
回収する薬品回収の改良方法である。
The present invention aims to efficiently absorb hydrogen sulfide and sulfur dioxide gas under the above conditions, and to use the alkali generated during the chemical recovery process in paper mills as a replenishing alkali for the alkali consumed by the absorption of hydrogen sulfide and sulfur dioxide gas. Hydrogen sulfide and sulfur dioxide gases that escape into the exhaust gas generated during the paper mill chemical recovery process, such as a recovery boiler, are absorbed using an alkaline aqueous solution, such as green liquor, white liquor, or weak liquor, and the absorbed liquid is 1
This is an improved method for recovering chemicals by extracting a portion and returning it to the chemical recovery process to effectively recover the sulfur content.

緑液とは薬品回収ボイラーで黒液を燃焼後の溶融物を水
又は弱液等で溶解した液である。
Green liquor is a liquid obtained by dissolving the molten material after burning black liquor in a chemical recovery boiler with water or weak liquid.

白液とはクラフトパルプ製造工場における薬品回収工程
で生じる緑液を清澄させ、その清澄液を苛性化工程で苛
性化した後の液である。
White liquor is a liquid obtained by clarifying green liquor produced in the chemical recovery process at a kraft pulp manufacturing plant, and causticizing the clarified liquor in a causticizing process.

弱液は、白液を含んだ石灰泥を洗浄した後の液であり、
白液の薄まったものである。
Weak liquid is the liquid after washing lime mud containing white liquor,
It is a diluted white liquor.

クラフトパルプ製造工場で生じる、緑液及び白液、弱液
の組成の−ψlを次に示す。
The -ψl of the compositions of green liquor, white liquor, and weak liquor produced in a kraft pulp manufacturing plant are shown below.

また、亜硫酸パルプ製造工場で生じる薬液としては、各
種の薬品回収方法において、硫化ソーダと炭酸ソーダの
混合液である緑液及び緑液を炭酸化した液また、少量の
硫化物等を含む炭酸ソーダ溶液がある。
In addition, chemical solutions generated in sulfite pulp manufacturing plants include green liquor, which is a mixture of sodium sulfide and soda carbonate, and carbonated solution of green liquor, as well as soda carbonate containing a small amount of sulfide, etc., in various chemical recovery methods. There is a solution.

それらの薬液の一例を次に示す。表−■ 緑液の組成の−fIlを示す。An example of those chemical solutions is shown below. Table -■ -fIl of the composition of green liquor is shown.

Na2Co3(mol / l ) 0.
99Na 2 S (mol / −e )
0.91Na2 so4(mol /−e )
0.19Na2 S203(mol /
l ) 0.07Na2So3(mol
/l ) 0.03表−■ 緑液を炭酸化した液の一例を示す。
Na2Co3 (mol/l) 0.
99Na2S (mol/-e)
0.91Na2so4(mol/-e)
0.19Na2 S203 (mol/
l) 0.07Na2So3 (mol
/l) 0.03 Table-■ An example of a carbonated green liquor is shown.

Na2CO3(mol /l ) 1゜4
ONa2S (mo1/l) 0.55N
a2SO4(mol /l ) 0.08
Na2 S20S2O5(/l ) 0.
05Na2SO3(mol / l )
0.02表−■ 少量の硫化物を含む炭酸ソーダ溶液の一例を示す。
Na2CO3 (mol/l) 1°4
ONa2S (mo1/l) 0.55N
a2SO4 (mol/l) 0.08
Na2 S20S2O5 (/l) 0.
05Na2SO3 (mol/l)
0.02 Table - ■ An example of a soda carbonate solution containing a small amount of sulfide is shown.

Na2CO3(mol /l ) 1.8
0Na2S (mol/A ) 0.
14Na 2 SO4(mol /l )
0.04Na2 s2o3(mol /l ’)
0.02Na2so 3 (rnol /
1. ) 0.01表■及び表■〜■に示
した様に薬品回収工程中の薬液を、アルカリ供給として
用いた場合、各薬液中に含まれる硫化ナトリウム(Na
2S)が吸収液中に入ることになり、吸収液中の硫化物
濃度が高くなって、遂には吸収液から硫化水素が発生し
てしまう。
Na2CO3 (mol/l) 1.8
0Na2S (mol/A) 0.
14Na 2 SO4 (mol/l)
0.04Na2 s2o3 (mol/l')
0.02Na2so3 (rnol/
1. ) 0.01 As shown in Table ■ and Tables ■ to ■, when the chemical solutions in the chemical recovery process are used as alkali supplies, the sodium sulfide (Na
2S) enters the absorption liquid, the sulfide concentration in the absorption liquid increases, and finally hydrogen sulfide is generated from the absorption liquid.

しかしこの場合、吸収液に供給される薬液の量が少な(
、吸収液に流入する硫化物の量が少ない場合は、吸収液
が吸収塔を通過する間に、ガス中の酸素と鉄、マンガン
、ニッケル、の触媒により液中硫化物が速やかに酸化さ
れ、液中の硫化物が処理されるため、硫化物を含む薬液
の供給による硫化水素の発生は無く、ガス中の硫化水素
及び亜硫酸ガスの吸収効果は持続する。
However, in this case, the amount of chemical solution supplied to the absorption solution is small (
When the amount of sulfide flowing into the absorption liquid is small, the sulfide in the liquid is quickly oxidized by the oxygen in the gas and the catalysts of iron, manganese, and nickel while the absorption liquid passes through the absorption tower. Since the sulfide in the liquid is treated, no hydrogen sulfide is generated due to the supply of a chemical solution containing sulfide, and the effect of absorbing hydrogen sulfide and sulfur dioxide gas in the gas continues.

また、吸収液への硫化物を含む薬液の供給の量が多くな
ると、ガス中の酸素量だけでは吸収液中の硫化物を処理
できずに鉄、マンガン、ニッケル、の硫化物が生じ、吸
収液からの硫化水素の発生がみられ、ガス中の硫化水素
の吸収効果は急速に悪くなる。
In addition, when the amount of chemical solution containing sulfide is supplied to the absorption liquid, the amount of oxygen in the gas alone cannot treat the sulfide in the absorption liquid, and sulfides of iron, manganese, and nickel are generated. Hydrogen sulfide is generated from the liquid, and the absorption effect of hydrogen sulfide in the gas deteriorates rapidly.

亜硫酸ガスは、この状態でもpHが前述の条件を維持し
ていれば、吸収効果は変わりな(持続する。
Even in this state, the absorption effect of sulfur dioxide gas remains unchanged (continues) as long as the pH maintains the above-mentioned conditions.

吸収液への硫化物を含む薬液の供給量が多く、吸収液か
らの硫化水素の発生、ガス中の硫化水素吸収効果の低下
が生じた場合でも、ガス中の酸素濃度を増加させるか、
吸収液の簡単な空気酸化をすることによって、液中の硫
化物を処理できる。
Even if a large amount of chemical solution containing sulfide is supplied to the absorption liquid and hydrogen sulfide is generated from the absorption liquid and the hydrogen sulfide absorption effect in the gas decreases, it is necessary to increase the oxygen concentration in the gas or
Sulfides in the liquid can be treated by simple air oxidation of the absorption liquid.

もちろん、この場合においても、吸収液中に前記触媒が
存在することが必要であり、触媒が無いと酸化装置が大
きくなり、また逆に空気により吸収液中からの硫化水素
の発生を促す結果ともなる。
Of course, in this case as well, it is necessary for the catalyst to be present in the absorption liquid; without the catalyst, the oxidation device will become larger, and conversely, air will promote the generation of hydrogen sulfide from the absorption liquid. Become.

吸収液への硫化物を含む薬液の供給量が多い場合、吸収
液の空気酸化をすることによって、薬液中の硫化ソーダ
は、チオ硫酸ソーダ又は芒硝(硫酸ソーダ)に変わり、
ガス中の硫化水素は吸収液に吸収されて、チオ硫酸ソー
ダ又は芒硝(硫酸ソーダ)に、亜硫酸ガスは亜硫酸ソー
ダ又は芒硝に変わる。
When a large amount of chemical liquid containing sulfide is supplied to the absorption liquid, the sodium sulfide in the chemical liquid is converted to sodium thiosulfate or sodium sulfate (sodium sulfate) by air oxidation of the absorption liquid.
Hydrogen sulfide in the gas is absorbed by the absorption liquid and turns into sodium thiosulfate or mirabilite (sodium sulfate), and sulfur dioxide gas turns into sodium sulfite or mirabilite.

これらの成分は抜出し液として炭酸ソーダ、酸性炭酸ソ
ーダと共に本プロセス外へ抜き出される。
These components are extracted from the process together with soda carbonate and acidic soda carbonate as an extraction liquid.

そして、薬品回収工程で使用される。本発明は亜硫酸パ
ルプ製造の薬品回収工程にも適用できるが、次に本発明
を組み込んだクラフトパルプ製造工場における薬品回収
工程の一例を図面によって説明する。
It is then used in the chemical recovery process. Although the present invention can also be applied to the chemical recovery process in sulfite pulp production, an example of the chemical recovery process in a kraft pulp manufacturing factory incorporating the present invention will be described below with reference to the drawings.

クラフトパルプ製造の薬品回収工程は、第4図に示す様
に、原料チップを蒸解工程でアルカリ性の蒸解液(白液
)で処理し残渣とパルプを得る。
In the chemical recovery process for producing kraft pulp, as shown in FIG. 4, raw material chips are treated with alkaline cooking liquor (white liquor) in the cooking process to obtain residue and pulp.

蒸解終了後、パルプ及び蒸解液をブロータンクヘブロー
した後洗浄工程へ送り、黒液とパルプに分離する。
After completion of cooking, the pulp and cooking liquor are blown into a blow tank and then sent to a washing process where they are separated into black liquor and pulp.

分離されたパルプは、スクリーンを経て次の工程へ送ら
れる。
The separated pulp is sent to the next process via a screen.

一方黒液は、濃縮工程を経て、薬品として再使用するた
め、回収ボイラでは黒液中の燃焼成分を燃焼させて有機
分を除き、有効薬品を分離回収する。
On the other hand, since the black liquor is reused as a medicine after going through a concentration process, a recovery boiler burns the combustion components in the black liquor, removes the organic components, and separates and recovers the effective medicine.

回収ボイラで得られた溶融物は、スメルトと呼ばれ弱液
に溶解されて緑液となる。
The molten material obtained in the recovery boiler is called smelt and is dissolved in weak liquid to become green liquor.

不溶解残渣を含む粗緑液はクラリファイヤ−でこれらを
除いた後、清澄緑液は苛性化工程へ送られる。
After the crude green liquor containing undissolved residues is removed in a clarifier, the clarified green liquor is sent to a causticizing process.

苛性化工程で清澄緑液は生石灰と混合、攪拌され、苛性
化反応を起して緑液中の炭酸ソーダが苛性ソーダに変わ
り白液となる。
In the causticizing process, the clear green liquor is mixed with quicklime and stirred to cause a causticizing reaction, where the soda carbonate in the green liquor turns into caustic soda and becomes white liquor.

白液は清澄後再び蒸解液として使用する。After clarification, the white liquor is used again as cooking liquor.

また、生石灰は苛性化工程で苛性化反応により石灰とな
るが、これは白液と分離後、洗浄された後キルンで焼か
れ、生石灰となり再び苛性化工程で使用される。
In addition, quicklime becomes lime through a causticizing reaction in the causticizing process, and this is separated from the white liquor, washed, and then burned in a kiln to become quicklime and used again in the causticizing process.

白液を含む石灰泥の洗浄後液を弱液といい、スメルトの
溶解に使われる。
The washed lime mud containing white liquor is called weak liquor and is used to dissolve smelt.

この様に薬品回収工程は、はとんどクローズドシステム
となっている。
In this way, the chemical recovery process is mostly a closed system.

しかし、実際は回収ボイラ等より硫化水素、亜硫酸ガス
として逃げるイオウ分の損失がある。
However, in reality, there is a loss of sulfur that escapes from recovery boilers as hydrogen sulfide and sulfur dioxide gas.

本方法は、とのイオウ分を回収し薬品回収工程内の薬品
バランスを崩さない方法である。
This method recovers the sulfur content of and does not disrupt the chemical balance in the chemical recovery process.

第4図の二点鎖線内が本発明プロセスである。The process of the present invention is shown within the chain double-dashed line in FIG.

まず、回収ボイラ排ガスをファンによって吸収塔に導き
、吸収液をポンプによって吸収塔頂へ送り、気液を向流
接触させ、排ガス中の硫化水素、亜硫酸ガスを吸収液に
吸収する。
First, the recovery boiler exhaust gas is guided to the absorption tower by a fan, and the absorption liquid is sent to the top of the absorption tower by a pump, the gas and liquid are brought into countercurrent contact, and the hydrogen sulfide and sulfur dioxide gas in the exhaust gas is absorbed into the absorption liquid.

アルカリ供給として、緑液または白液もしくは弱液を循
環タンクへ供給する。
Green liquor or white liquor or weak liquor is supplied to the circulation tank as the alkaline supply.

循環タンクは、空気で曝気が行なわれている。The circulation tank is aerated with air.

触媒は触媒タンクより循環タンクに供給する。また吸収
液の1部は抜出して薬品回収工程、即ち黒液濃縮工程、
回収ボイラ工程、苛性化工程等へ戻すことができる。
The catalyst is supplied from the catalyst tank to the circulation tank. In addition, a part of the absorption liquid is extracted and used in the chemical recovery process, that is, the black liquor concentration process.
It can be returned to the recovery boiler process, causticizing process, etc.

しかし望ましくは、アルカリ供給用として緑液を用いた
場合は緑液を取り出した個所へ、白液、弱液についても
同様にそれらを取り出した個所へ戻すのが種々の観点よ
り合理的である。
However, desirably, when green liquor is used to supply alkali, it is rational from various points of view to return the green liquor to the place from which it was taken out, and to return the white liquor and weak liquor to the place from which they were taken out as well.

また、戻された液中のチオ硫酸ソーダ、芒硝、亜硫酸ソ
ーダは、薬品回収工程中の回収ボイラエ程で処理され、
硫化ソーダ及び炭酸ソーダとなるため、系内で蓄積され
ることはない。
In addition, sodium thiosulfate, mirabilite, and sodium sulfite in the returned liquid are treated in the recovery boiler step during the chemical recovery process.
Since it becomes soda sulfide and soda carbonate, it does not accumulate in the system.

以下実施例について説明する。Examples will be described below.

実施例 1 硫化水素、亜硫酸ガスを吸収除去する際、アルカリ供給
液として緑液を用い、吸収液に触媒として硫酸ニッケル
を添加したアルカリ性水溶液を使用し、且つ吸収液槽に
空気曝気を行った場合の実施例を示す。
Example 1 When hydrogen sulfide and sulfur dioxide gas are absorbed and removed, green liquor is used as the alkaline supply liquid, an alkaline aqueous solution containing nickel sulfate as a catalyst is used in the absorption liquid, and the absorption liquid tank is aerated with air. An example is shown below.

緑液は吸収液循環槽に供給したが、吸収液槽からの硫化
水素の発生は全く無く、また排ガス中の硫化水素及び亜
硫酸ガスの除去効果は第1図に示した様に良い結果が得
られた。
The green liquor was supplied to the absorption liquid circulation tank, but no hydrogen sulfide was generated from the absorption liquid tank, and good results were obtained in removing hydrogen sulfide and sulfur dioxide gas from the exhaust gas, as shown in Figure 1. It was done.

実施例1の場合の抜出し吸収液の組成を次に示す。The composition of the extracted absorption liquid in Example 1 is shown below.

抜出し戻し液 Na2CO30,238mol/1 NaHC03o、869 〃 Na2S2O30,3601! Na2SO30,397〃 Na2SO40,010tt 液量 5.4 l/H 実施例 2 硫化水素、亜硫酸ガスを吸収除する際、アルカリ供給液
として緑液を用い、吸収液に触媒として硫酸第一鉄及び
硫酸マンガンを同時に添加したアルカリ水溶液を使用し
、且つ吸収液槽に空気曝気を行った場合の実施例を示す
Extracted and returned liquid Na2CO30, 238 mol/1 NaHC03o, 869 〃 Na2S2O30, 3601! Na2SO30,397〃 Na2SO40,010tt Liquid volume 5.4 l/H Example 2 When absorbing and removing hydrogen sulfide and sulfur dioxide gas, green liquor was used as the alkali supply liquid, and ferrous sulfate and manganese sulfate were used as catalysts in the absorption liquid. An example will be shown in which an alkaline aqueous solution to which was added at the same time was used, and the absorption liquid tank was aerated with air.

緑液供給による吸収液循環槽からの硫化水素の発生は全
く認められなかった。
No generation of hydrogen sulfide was observed from the absorption liquid circulation tank due to green liquor supply.

また排ガス中の硫化水素及び亜硫酸ガスの除去効果を第
2図に示した。
Furthermore, the effect of removing hydrogen sulfide and sulfur dioxide gas in exhaust gas is shown in Figure 2.

実施例2の場合の抜出し吸収液の組成を次に示す。The composition of the extracted absorption liquid in Example 2 is shown below.

抜出し戻し液 Na COO,236rnl/1 3 NaHCo 0.864 〃Na2S2O
30,421tt NaSo 0.331 l!3 Na SO’0.010 // 4 液量 8.I J/H 実施例1及び2で用いた吸収塔として充填塔を使用した
Extraction and return liquid Na COO, 236rnl/1 3 NaHCo 0.864 〃Na2S2O
30,421tt NaSo 0.331 l! 3 Na SO'0.010 // 4 Liquid amount 8. I J/H As the absorption tower used in Examples 1 and 2, a packed tower was used.

本実施例1及び2の概略フローシートを第3図に示した
A schematic flow sheet for Examples 1 and 2 is shown in FIG.

実施例 3 硫化水素、亜硫酸ガスを吸収除去する際、アルカリ供給
液として弱液な用い、吸収液に触媒として硫酸マンガン
を添加したアルカリ水溶液を使用し、且つ吸収液槽に空
気曝気を行った場合の実施例を示す。
Example 3 When hydrogen sulfide and sulfur dioxide gas are absorbed and removed, a weak liquid is used as the alkaline supply liquid, an alkaline aqueous solution containing manganese sulfate as a catalyst is used in the absorption liquid, and the absorption liquid tank is aerated with air. An example is shown below.

弱液は吸収液循環槽に供給したが、吸収液槽からの硫化
水素の発生ゆ全く無かった。
The weak liquid was supplied to the absorption liquid circulation tank, but there was no generation of hydrogen sulfide from the absorption liquid tank.

この実施例では吸収塔として6段の自皿塔な用いたが、
H2S、SO□の除去効果は良(,24時間運転中のH
2S除去率は90%、SO2の除去率は95%程度であ
った。
In this example, a 6-stage self-plate tower was used as the absorption tower.
The removal effect of H2S and SO□ is good (, H2S during 24-hour operation
The 2S removal rate was 90%, and the SO2 removal rate was about 95%.

実施例3の場合の抜出し吸収液の組成を次に示す。The composition of the extracted absorption liquid in Example 3 is shown below.

抜出し戻し液 Na2CO30,102Cmol/A’)Na2CO3
o、 612 Crnol / −e ”JNa2S
203 0.323 〔mol/l〕Na2SO30,
235〔mol/l〕 Na2SO40,125Cmol/Al 液量 5 1/H) 実施例 4 硫化水素、亜硫酸ガスを吸収除去する際、アルカリ供給
液として弱液を用い、吸収液に触媒として塩化第二鉄を
添加したアルカリ水溶液を使用し、且つ吸収液槽に空気
曝気を行った場合の実施例を示す。
Extraction and return liquid Na2CO30,102Cmol/A')Na2CO3
o, 612 Crnol/-e”JNa2S
203 0.323 [mol/l] Na2SO30,
235 [mol/l] Na2SO40,125Cmol/Al Liquid volume 5 1/H) Example 4 When absorbing and removing hydrogen sulfide and sulfur dioxide gas, a weak liquid was used as the alkaline supply liquid, and ferric chloride was added as a catalyst to the absorption liquid. An example will be shown in which an aqueous alkali solution containing .

弱液は吸収液循環槽に供給したが、吸収液槽からの硫化
水素の発生は全(無かった。
The weak liquid was supplied to the absorption liquid circulation tank, but no hydrogen sulfide was generated from the absorption liquid tank.

この実施例では吸収塔として6段の目皿基を用いたが、
H2S、S02の除去効果は良く、24時間運転中のH
2S除去率は90%、SO2の除去率は95%程度であ
った。
In this example, a six-stage perforated plate base was used as the absorption tower.
The removal effect of H2S and S02 is good, and H2S and S02 are removed during 24-hour operation.
The 2S removal rate was 90%, and the SO2 removal rate was about 95%.

実施例4の場合の抜出し吸収液の組成を次に示す。The composition of the extracted absorption liquid in Example 4 is shown below.

抜出し戻し液 Na2CO30,095Cmol /l 〕NaHC0
3o、 552 (mol /l: )Na2S、、
03 0.340 Cmol / l ’JNa2
5o3o、 103 Cmol /l )Na2so
4 o、260 Cmol/l)実施例 5 硫化水素、亜硫酸ガスを吸収除去する際、アルカリ供給
液として弱液を用い、吸収液に触媒として硫酸第二鉄を
添加したアルカリ水溶液を使用し、且つ吸収液槽に空気
曝気を行った場合の実施例を示す。
Extraction and return liquid Na2CO30,095Cmol/l ]NaHC0
3o, 552 (mol/l: )Na2S,,
03 0.340 Cmol/l'JNa2
5o3o, 103 Cmol/l) Na2so
4 o, 260 Cmol/l) Example 5 When absorbing and removing hydrogen sulfide and sulfur dioxide gas, a weak liquid was used as the alkaline supply liquid, an alkaline aqueous solution to which ferric sulfate was added as a catalyst was used in the absorption liquid, and An example is shown in which air aeration is performed in the absorption liquid tank.

弱液は吸収液循環槽に供給したが、吸収液槽からの硫化
水素の発生は全(無かった。
The weak liquid was supplied to the absorption liquid circulation tank, but no hydrogen sulfide was generated from the absorption liquid tank.

この実施例では吸収塔として3段の目皿基を用いたが、
このときのH2S除去率は60〜70%と悪かった。
In this example, a three-stage perforated plate base was used as the absorption tower.
The H2S removal rate at this time was as poor as 60-70%.

そこで目皿を6段に増してもとと同じにしたらH2S1
S02の除去効果もよくなり、H2Sで90%、S02
は95%程度が得られた。
So, if I increase the perforation plate to 6 levels and keep it the same as before, H2S1
The removal effect of S02 is also improved, 90% with H2S, S02
About 95% was obtained.

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

第1図は実施例1の場合のH2S、SO2吸収除去率を
示し、第2図は実施例2の場合のH2S、SO2除去率
を示すものであり、第3図は実施例1及び2の概略フロ
ーシートを示す。 第4図は本発明を組み込んだクラフトパルプ製造薬品回
収工程図である。 1・・・・・・吸収塔入口ガス、2・・・・・・吸収塔
出口ガス、3・・・・・・吸収塔、4・・・・・・吸収
液循環槽、5・・・・・・吸収液、6・・・・・・抜出
し液、7・・・・・・緑液、8・・・・・・緑液槽、9
・・・・・・空気、10・・・・・・白液、11・・・
・・・弱液、12・・・・・・ブロア、13・・・・・
・触媒、14・・・・・・触媒槽、15・・・・・・原
料チップ、16・・・・・・蒸解工程、17・・・・・
・洗浄工程、18・・・・・・スクリーン、19・・・
・・・濃縮工程、20・・・・・・回収ボイラ一工程、
21・・・・・・苛性化工程、22・・・・・・キルン
、23・・・・・・電気集塵機、24・・・・・・煙突
、25・・・・・・未晒しパルプ、26・・・・・・黒
液、27・・・・・・スメルト、28・・・・・・石灰
(CaCO3)、29・・・・・・生石灰(Cab)、
A:アルカリ供給として緑液を用いた場合の吸収後液の
戻り、B:アルカリ供給として白液を用いた場合の吸収
後液の戻り、C:アルカリ供給として弱液を用いた場合
の吸収後液の戻り。
Figure 1 shows the H2S and SO2 absorption and removal rates in Example 1, Figure 2 shows the H2S and SO2 removal rates in Example 2, and Figure 3 shows the H2S and SO2 removal rates in Example 1 and 2. A schematic flow sheet is shown. FIG. 4 is a diagram of a kraft pulp manufacturing chemical recovery process incorporating the present invention. 1... Absorption tower inlet gas, 2... Absorption tower outlet gas, 3... Absorption tower, 4... Absorption liquid circulation tank, 5... ... Absorption liquid, 6 ... Extraction liquid, 7 ... Green liquid, 8 ... Green liquid tank, 9
...Air, 10...White liquid, 11...
...Weak liquid, 12...Blower, 13...
・Catalyst, 14... Catalyst tank, 15... Raw material chips, 16... Cooking process, 17...
・Cleaning process, 18...Screen, 19...
... Concentration step, 20 ... Recovery boiler 1 step,
21... Causticizing process, 22... Kiln, 23... Electrostatic precipitator, 24... Chimney, 25... Unbleached pulp, 26...black liquor, 27...smelt, 28...lime (CaCO3), 29...quicklime (Cab),
A: Return of liquid after absorption when green liquor is used as alkali supply, B: Return of liquid after absorption when white liquor is used as alkali supply, C: After absorption when weak liquid is used as alkali supply. Return of liquid.

Claims (1)

【特許請求の範囲】[Claims] 1 製紙工場における薬品回収工程において、当該薬品
回収工程内で生じるアルカリ性薬液を使用し)て、回収
ボイラ等製紙工場の薬品回収工程から生じる排ガス中に
逃げる硫化水素、亜硫酸ガスを吸収し、該イオウ分を回
収する方法において、マンガン、ニッケルの各塩類を単
独に、または鉄、マンガン、ニッケルの各塩類のうち2
種以上の混合物を触媒として添加した上記アルカリ性水
溶液を吸収液として、pH8,3〜pH10,0の範囲
で用い、硫化水素、亜硫酸ガスを吸収せしめることを特
徴とする製紙工場における薬品回収工程の改良方法。
1. In the chemical recovery process at a paper mill, the alkaline chemical solution generated during the chemical recovery process is used to absorb hydrogen sulfide and sulfur dioxide gas that escapes into the exhaust gas generated from the paper mill's chemical recovery process, such as a recovery boiler, and remove the sulfur. In the method of recovering manganese and nickel salts, or two of each of iron, manganese and nickel salts,
An improvement in the chemical recovery process in a paper mill, characterized in that the above-mentioned alkaline aqueous solution to which a mixture of at least 1 species is added as a catalyst is used as an absorption liquid in a pH range of 8.3 to 10.0 to absorb hydrogen sulfide and sulfur dioxide gas. Method.
JP51121286A 1976-10-12 1976-10-12 Improved methods for chemical recovery in paper mills Expired JPS5943600B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51121286A JPS5943600B2 (en) 1976-10-12 1976-10-12 Improved methods for chemical recovery in paper mills

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51121286A JPS5943600B2 (en) 1976-10-12 1976-10-12 Improved methods for chemical recovery in paper mills

Publications (2)

Publication Number Publication Date
JPS5349102A JPS5349102A (en) 1978-05-04
JPS5943600B2 true JPS5943600B2 (en) 1984-10-23

Family

ID=14807487

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51121286A Expired JPS5943600B2 (en) 1976-10-12 1976-10-12 Improved methods for chemical recovery in paper mills

Country Status (1)

Country Link
JP (1) JPS5943600B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5149488B2 (en) * 2006-02-23 2013-02-20 メタウォーター株式会社 Pyrolysis gas treatment method
CN103304013B (en) * 2013-05-20 2014-10-15 秦小林 Process method for treating alkyl chloride waste water by using mancozeb

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5310374A (en) * 1976-07-15 1978-01-30 Ebara Corp Removing method for hydrogen sulfide and sulfur dioxide contained in exhaust gas

Also Published As

Publication number Publication date
JPS5349102A (en) 1978-05-04

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