JPS58202021A - Treatment of hydrogen sulfide-containing gas - Google Patents

Treatment of hydrogen sulfide-containing gas

Info

Publication number
JPS58202021A
JPS58202021A JP57086158A JP8615882A JPS58202021A JP S58202021 A JPS58202021 A JP S58202021A JP 57086158 A JP57086158 A JP 57086158A JP 8615882 A JP8615882 A JP 8615882A JP S58202021 A JPS58202021 A JP S58202021A
Authority
JP
Japan
Prior art keywords
hydrogen sulfide
gas
liquid
treatment
caustic soda
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
JP57086158A
Other languages
Japanese (ja)
Inventor
Shigeo Kobayashi
繁夫 小林
Shiyuuji Arita
収次 有田
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.)
Unitika Ltd
Original Assignee
Unitika 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 Unitika Ltd filed Critical Unitika Ltd
Priority to JP57086158A priority Critical patent/JPS58202021A/en
Publication of JPS58202021A publication Critical patent/JPS58202021A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To carry out the treatment of a hydrogen sulfide-containing gas stably and economically in good efficiency, by a method wherein a gas absorbing liquid having hydrogen sulfide absorbed thereby is treated with potassium hydroxide and the obtained treating liquid is reused in the alkali treatment of the hydrogen sulfide-containing gas. CONSTITUTION:A hydrogen sulfide-containing gas 3 is brought into contact with an aqueous caustic soda solution 5 in a catalytic reaction tower 1 while a gas absorbing liquid 7 is sent to a storage tank 8 to be stored therein. This gas absorbing liquid 7 is heated by a heat exchanger 10 to be supplied to a treating tank 11 while an aqueous potassium hydroxide solution is supplied thereto from the storage tank 12 to treat said absorbing liquid 7. The treated liquid is filtered by a filter apparatus 14 to remove calcium carbonate and a treating liquid 15 comprising sodium sulfide and caustic soda is obtained. This treating liquid 15 is sent to a storage tank 16 to be mixed with the absorbing liquid 7 and the ratio of sodium sulfide and caustic soda is adjusted to 0.6-1.2. Subsequently, this treating liquid is sent to the reaction tower 1 and added to the aqueous caustic soda solution 5 to be reused.

Description

【発明の詳細な説明】 って効率よく、安定かつ経済的に処理する方法に関する
ものである。
DETAILED DESCRIPTION OF THE INVENTION This invention relates to an efficient, stable and economical processing method.

従来硫化水素含有ガスを例えば苛性ソーダ水溶液と接触
せしめて硫化水素を吸収除去する方法は処理操作が比較
的簡単であることから広く用いられている。
Conventionally, a method of absorbing and removing hydrogen sulfide by contacting a hydrogen sulfide-containing gas with, for example, an aqueous solution of caustic soda has been widely used because the treatment operation is relatively simple.

しかし、この方法は、硫化水素と苛性ソーダを接触させ
た場合、空気中の炭酸ガスも苛性ソーダと接触して反応
するため、大量の苛性ソーダが消費され、実質的に硫化
水素の吸収除去の障害となり経済的に硫化水素?処理す
ることが難かしい。
However, in this method, when hydrogen sulfide and caustic soda are brought into contact, carbon dioxide gas in the air also comes into contact with the caustic soda and reacts, so a large amount of caustic soda is consumed, which essentially becomes an obstacle to the absorption and removal of hydrogen sulfide and is economical. Hydrogen sulfide? Difficult to process.

特にガス中の硫化水素の濃度が低い場合には、炭酸ガス
により消費される苛性ソーダの畳が増加し、更に硫化水
素全吸収除去しようとして硫化水素含有ガスと苛性ソー
ダとの接触時間を長くすると、炭酸ガスと苛性ソーダと
の反応も進み、炭酸ガスにより消費される苛性ソーダの
量は著しく増大する。
In particular, when the concentration of hydrogen sulfide in the gas is low, the amount of caustic soda consumed by carbon dioxide gas increases, and if the contact time between hydrogen sulfide-containing gas and caustic soda is increased in an attempt to completely absorb and remove hydrogen sulfide, carbon dioxide The reaction between the gas and caustic soda also progresses, and the amount of caustic soda consumed by carbon dioxide gas increases significantly.

しかも、この方法による場合、生成するアルカリ廃液に
は、硫化ソーダ( Na,S) 、水硫化ソーダ(Na
51→及び炭酸ソーダ(N a to 0B )等が含
まれているので、このアルカリ廃液をそのまま廃棄する
訳にはいかず・その処理が問題となる。即ちかかる成分
を含有するアルカリ廃液の処理としては、クラウス法、
或いは酸分解して純度の高いNaSHとじて回収する方
法等があるが、これらの方法はアルカリ廃液中の炭酸ソ
ーダの分解により発生する炭酸ガスが障害となって処理
コストが高く、かつ安定した連続運転が困難である等の
欠点を有している。
Moreover, when using this method, the alkaline waste liquid produced contains sodium sulfide (Na,S) and sodium hydrogen sulfide (Na
51→ and soda carbonate (N a to 0B ), etc., this alkaline waste liquid cannot be disposed of as it is, and its disposal becomes a problem. In other words, for the treatment of alkaline waste liquid containing such components, the Claus method,
Alternatively, there are methods such as acid decomposition and recovery of highly pure NaSH, but these methods are expensive due to the carbon dioxide gas generated by the decomposition of sodium carbonate in the alkaline waste liquid, and are difficult to maintain in a stable continuous manner. It has drawbacks such as being difficult to drive.

このため本出願人は先にアルカリ廃液に鉱酸を添加して
含有硫黄化合物會硫化水業ガスにして除去し、これ?燃
焼する方法(特開昭52−152873号公報)を提案
した。しかし、この方法はアルカリ廃液の処理方法とし
ては優れた効果を有するものであるが、ガス吸収液中に
は多量の炭酸ソーダが含まれているため鉱酸の消費量が
多く、また炭酸ガス濃度が高いため安定した燃焼が得ら
れないという問題が残されていた。
For this reason, the applicant first added a mineral acid to the alkaline waste liquid to remove the sulfur compounds contained therein by turning it into a sulfurized water gas. A combustion method (Japanese Patent Laid-Open No. 152873/1983) was proposed. However, although this method has excellent effects as a treatment method for alkaline waste liquid, it consumes a large amount of mineral acid because the gas absorption liquid contains a large amount of soda carbonate, and the carbon dioxide concentration also increases. The problem remained that stable combustion could not be obtained due to the high

本発明は上述の如き従来のアルカリ処理による硫化水素
含有ガスの吸収除去方法における問題点を踏まえ硫化水
素の吸収除去及びガス吸収液の処理の両面から解決を図
ったものであり、その目的とするところは硫化水素含有
ガス全アルカリ処理して吸収除去する方法において硫化
水素含有ガスヶ効率よく、安定かつ経済的に処理すると
共に得られるガス吸収液を容易に、しかも経済的に処理
することにある。
The present invention aims to solve the problems in the conventional method of absorbing and removing hydrogen sulfide-containing gas by alkaline treatment as described above, and has aimed to solve the problems from both the absorption and removal of hydrogen sulfide and the treatment of the gas absorption liquid. The object of the present invention is to treat hydrogen sulfide-containing gas efficiently, stably, and economically in a method for absorbing and removing hydrogen sulfide-containing gas through total alkali treatment, and to process the resulting gas absorption liquid easily and economically.

即ち、本発明は、硫化水素含有ガスを苛性アルカリ水溶
液でアルカリ処理し、硫化水1に吸収除去する方法にお
いて前記硫化水素?吸収したガス吸収液全水酸化カルシ
ウムで処理した後濾過し、得らnた処理液を硫化水素濃
度ガスのアルカリ処理に再使用することを特徴とする硫
化水素含有ガスの処理方法である。
That is, the present invention provides a method for alkali-treating hydrogen sulfide-containing gas with an aqueous caustic alkali solution and absorbing and removing the hydrogen sulfide-containing gas into sulfide water 1. This is a method for treating hydrogen sulfide-containing gas, which is characterized in that the absorbed gas absorption liquid is treated with all calcium hydroxide and then filtered, and the resulting treated liquid is reused for alkaline treatment of hydrogen sulfide-concentrated gas.

以下、本発明?更に詳細に説明する〇 先づ本発明における硫化水素含有ガスを吸収したガス吸
収液としては、通常の硫化水素含有ガスを苛性ソーダ硫
化ソーダ等のアルカリ水溶液と接触ゼしめて吸収除去し
た液があげられ、その吸収除去した液中には、硫化ソー
ダ(Na、S)、水硫化ソーダQJaS)9及び同時に
空気中の炭酸ガスが苛性ソーダ等と反応して生成した炭
酸ソーダ(NatCOa)も含有されている。
Is this invention the following? More detailed explanation: First, the gas absorption liquid that has absorbed hydrogen sulfide-containing gas in the present invention includes a liquid that is obtained by absorbing and removing ordinary hydrogen sulfide-containing gas by contacting and gelling it with an alkaline aqueous solution such as caustic soda and sodium sulfide. The absorbed and removed liquid also contains sodium sulfide (Na, S), sodium hydrogen sulfide QJaS) 9 and at the same time, sodium carbonate (NatCOa) produced by the reaction of carbon dioxide gas in the air with caustic soda and the like.

従来、このガス吸収液は、これを無害化して廃棄するか
、又は、そのままアルカリ処理に再供給していたが、本
発明方法においてはこ庇を水酸カルシウムで処理して処
理液としてアルカリ処理に再使用するものである。即ち
、前記ガス吸収液は先づ水酸化カルシウムで処理さnる
。この場合、使用する水酸化カルシウムは濃度15〜3
0%の水溶液とすることが好適である。また、この場合
の処理温度は低温では処理に長時間を要するので90〜
100℃の温度で行うことが好ましい。なお処理時間は
水酸化カルシウムの添加量、処理温度にもよるが15〜
60分程度で充分である。
Conventionally, this gas absorption liquid was either rendered harmless and disposed of, or re-supplied as is for alkaline treatment, but in the method of the present invention, the eaves are treated with calcium hydroxide and used as a treatment liquid for alkaline treatment. It is intended to be reused. That is, the gas absorption liquid is first treated with calcium hydroxide. In this case, the concentration of calcium hydroxide used is 15-3
A 0% aqueous solution is preferable. In addition, the processing temperature in this case is 90 - 90°C because it takes a long time to process at low temperatures.
Preferably it is carried out at a temperature of 100°C. Although the treatment time depends on the amount of calcium hydroxide added and the treatment temperature, it is 15~
About 60 minutes is sufficient.

このようにして水酸化カルシウムで処理されたガス吸収
液には、硫化ソーダCN&tS) 、苛性ソーダ(Na
OH)及び炭酸カルシウム(OaOOA)が生成される
ので1これk濾過して炭酸カルシウム(C!aOOj)
 t”除去し、処理液とする。
The gas absorption liquid treated with calcium hydroxide in this way contains sodium sulfide (CN&tS), caustic soda (Na
Since OH) and calcium carbonate (OaOOA) are generated, filter this to remove calcium carbonate (C!aOOj).
t” is removed and used as a processing solution.

かぐして得らnた処理液はそのまま或いはガス吸収液の
一部と混合した後、更に苛性ソーダを加えて硫化水素含
有ガスのアルカリ処理に再使用する。
The treatment liquid obtained by smelting is used as it is or after being mixed with a part of the gas absorption liquid, and then caustic soda is added thereto and reused for alkali treatment of hydrogen sulfide-containing gas.

従来の硫化水素ガスII−吸収したガス吸収液をそのま
ま循環して使用する場合には、ガス吸収液中には多量の
炭酸ソーダが含まれているが本発明方法ニオいては、ガ
ス吸収液を水酸化カルシウムで処理した処理液?循環使
用するものであるからガス吸収液中の炭酸ソーダの平衡
濃度を低くすることができ、従って、アルカリ処理中に
炭酸ソーダの結晶によるトラブルがなく、しかも処理液
中には苛性ソーダが含まれているので、新たに添加する
苛性ソーダの量を約40%程度少なくすることができる
When the conventional hydrogen sulfide gas II-absorbed gas absorption liquid is circulated and used as it is, the gas absorption liquid contains a large amount of soda carbonate, but in the method of the present invention, the gas absorption liquid is Treatment solution treated with calcium hydroxide? Since it is recycled, the equilibrium concentration of sodium carbonate in the gas absorption liquid can be lowered, and therefore there is no trouble caused by crystals of soda carbonate during alkali treatment, and the treatment liquid does not contain caustic soda. Therefore, the amount of newly added caustic soda can be reduced by about 40%.

特に、処理液の使用量?得らnるガス吸収液の中の硫化
ソーダと水硫化ソーダとの比(NaSH/Na、s)が
α6〜L2となるように丁nば苛性ソーダと炭酸ガスと
の反応が抑制され、硫化水素含有ガスとの反応が優先す
るため、排ガス中の硫化水素の吸収除去量が増大し、処
理排ガス中の硫化水素濃度k 2 ppm以下とするこ
とができると共に炭酸ガスにより消費される苛性ソーダ
の量全減少せしめることができる。
Especially the amount of processing liquid used? If the ratio of sodium sulfide to sodium hydrogen sulfide (NaSH/Na, s) in the obtained gas absorption liquid is α6~L2, the reaction between caustic soda and carbon dioxide gas is suppressed, and hydrogen sulfide is Since the reaction with the contained gas takes priority, the amount of hydrogen sulfide absorbed and removed from the exhaust gas increases, making it possible to reduce the hydrogen sulfide concentration in the treated exhaust gas to below k 2 ppm, and to reduce the total amount of caustic soda consumed by carbon dioxide gas. can be reduced.

このようにして処理液をアルカリ処理に使用して得られ
るガス吸収液は上記の如(水酸化力ルシラムで処理し再
び処理液として循環使用することができる。また、処理
液を循環使用する場合は循環量會排ガス中の炭酸ガスで
消費される量に対応するように調整することによりガス
吸収液をそのまま循環使用する場合に比して炭酸ソーダ
の平衡濃度を低下することができるので、安定してアル
カリ処理を行うことができる。
The gas-absorbing liquid obtained by using the treatment liquid in the alkaline treatment in this way can be treated with luciram hydroxide and recycled as a treatment liquid as described above.Also, when the treatment liquid is recycled By adjusting the circulation amount to correspond to the amount consumed by carbon dioxide in the exhaust gas, the equilibrium concentration of soda carbonate can be lowered compared to when the gas absorption liquid is recycled as it is, so it is stable. Alkaline treatment can be carried out.

なお、処理液上循環使用した場合に得られる過剰のガス
吸収液には多量の炭酸ソーダが含まれていないから上述
したクラウス法或いは酸分解してNa5Hとして回収す
る方法等によってもこn’f処理することができる。ま
たガス吸収液全上述の鉱酸によってその含有硫黄化合物
を硫化水素ガスとして除去しこれを燃焼して処理する場
合にも、鉱酸の消費量が少くて済み、また硫化水素ガス
が安定に発生し、炭酸ガスが少いので燃焼がスムースに
行える利点がある。
In addition, since the excess gas absorption liquid obtained when circulating above the treatment liquid does not contain a large amount of sodium carbonate, this n'f treatment can also be carried out by the above-mentioned Claus method or the method of acid decomposition and recovery as Na5H. can do. In addition, when the sulfur compounds contained in the gas absorption liquid are removed as hydrogen sulfide gas using the above-mentioned mineral acid and then burned and treated, the amount of mineral acid consumed is small, and hydrogen sulfide gas is stably generated. However, it has the advantage of being able to burn smoothly as it contains less carbon dioxide.

なお、前記処理液と炉別した炭酸カルシウムは酸性排水
の中和に利用してもよく、また、通常の方法ニより再生
して水酸化カルシウムとし、ガス吸収液の処理に使用し
てもよい。
Incidentally, the calcium carbonate separated from the treatment liquid in the furnace may be used for neutralizing acidic wastewater, or it may be regenerated into calcium hydroxide using a normal method and used for the treatment of gas-absorbing liquid. .

次に本発明方法金添付図面により更に説明する。Next, the method of the present invention will be further explained with reference to the accompanying drawings.

図は本発明方法の一例を示すフロー概略図であり、図に
おいて接触反応塔(11には苛性ソーダ水溶液の流下速
度全抑制するため充填物(2)が充填されている。硫化
水嚢含有ガス(3)ニ供給さnる苛性ソーダ水溶液と接
触反応塔(1)内で接触してガス中の    ゛硫黄化
合物と炭酸ガスが吸収除去さn、処理排ガス(6)とし
てそのまま廃棄さnる。
The figure is a flow diagram showing an example of the method of the present invention. In the figure, the contact reaction tower (11 is filled with a packing (2) to completely suppress the flow rate of the caustic soda aqueous solution. The sulfide water sac-containing gas ( 3) The gas is brought into contact with the supplied caustic soda aqueous solution in the contact reaction tower (1), and the sulfur compounds and carbon dioxide gas in the gas are absorbed and removed, and the gas is disposed of as treated exhaust gas (6).

一方、苛性ソーダ水溶液はガス中の硫黄化合物、炭酸ガ
スを吸収し、硫化ソーダ、水硫化ソーダ。
On the other hand, an aqueous solution of caustic soda absorbs sulfur compounds and carbon dioxide gas in the gas, producing sodium sulfide and sodium hydrogen sulfide.

炭酸ソーダ等を形成し、ガス吸収液(71として定量ポ
ンプ(4)により貯蔵タンク(8)に送られ、貯蔵され
る。
Sodium carbonate and the like are formed and sent as a gas absorption liquid (71) to a storage tank (8) by a metering pump (4) and stored therein.

次いでこのガス吸収液(7)全定量ポンプ(9)ヲ通し
た後、熱交換器QGによシ加熱して処理槽0υに供給し
、同時に貯蔵タンク(121から水酸化カルシウム水溶
液を定量ポンプnaueより供給して処理すると・硫化
ソーダ及び苛性ソーダが上澄液として、また炭酸カルシ
ウムが沈澱物として得られるので1これ1k濾過装置(
141で洲過して炭酸カルシウムを除太し、処理液a5
1とする。
Next, this gas absorption liquid (7) is passed through the metering pump (9), heated by the heat exchanger QG and supplied to the processing tank 0υ, and at the same time, the calcium hydroxide aqueous solution is passed through the metering pump naue from the storage tank (121).・Soda sulfide and caustic soda are obtained as a supernatant liquid, and calcium carbonate is obtained as a precipitate.
141 to remove the calcium carbonate, and process liquid A5.
Set to 1.

かくして得られた処理液Q51は一旦、貯蔵タンクC1
61に送り、次いで定量ポンプ(17)によシ連続的に
送液し、ガス吸収液(7)と混合した後、定量ポンプO
Sによシ送液し、更に苛性ソーダ水溶液(5)?加えて
、硫化水素含有ガスのアルカリ処理に再使用する。
The treatment liquid Q51 thus obtained is temporarily stored in the storage tank C1.
61, then continuously fed to the metering pump (17), mixed with the gas absorption liquid (7), and then fed to the metering pump O.
The solution is sent to S, and then the caustic soda aqueous solution (5)? In addition, it will be reused for alkaline treatment of hydrogen sulfide-containing gas.

この場合、処理液の供給量?、得らnるガス吸収液中の
硫化ソーダと水硫化ソーダとの比(Na5H/Na1S
 )が0.6〜L2となるようにすれば、硫化水素含有
ガス(3)中の硫黄化合物を効率よく吸収除去すること
ができ、かつ炭酸ガスにより消費される苛性ソーダ量を
減少せしめることができる。
In this case, what is the supply amount of processing liquid? , the ratio of sodium sulfide to sodium hydrogen sulfide in the obtained gas absorption liquid (Na5H/Na1S
) is 0.6 to L2, the sulfur compounds in the hydrogen sulfide-containing gas (3) can be efficiently absorbed and removed, and the amount of caustic soda consumed by carbon dioxide gas can be reduced. .

一方、濾過装置(14+で炉別された炭酸カルシウムは
県外に取出す。
On the other hand, calcium carbonate that has been separated by a filtration device (14+) is taken out of the prefecture.

なお、過剰のガス吸収液は貯蔵タンク(8)から取出し
、廃棄処理装置(図示せず)に送シ、硫酸を添加して、
含有硫黄化合物を硫化水素ガスとして除去し1こn2燃
焼して処理する。
In addition, the excess gas absorption liquid is taken out from the storage tank (8), sent to a waste treatment device (not shown), and sulfuric acid is added thereto.
The sulfur compounds contained are removed as hydrogen sulfide gas and treated by combustion.

以上述べた如く、本発明方法は一硫化水素含有ガス全了
ルカリ水溶液でアルカリ処理して硫化水素全吸収除去す
る方法において、硫化水素を吸収したガス吸収液?、水
酸化カルシウムで処理して得られた処理液を硫化本案含
有ガスのアルカリ処理に再使用するものであるから、従
来のガス吸収液全単独で循環使用する場合に比してガス
吸収液中の炭酸ソーダの平衡濃度全低下することができ
、アルカリ処理時における炭酸ソーダの結晶によるトラ
ブルがなく、また処理液中には苛性ソーダが含まnでい
るので新たに添加するアルカリ水溶液の量も少くて済み
、従って安定かつ経済的にアルカリ処理ケ行うことがで
き、本発明方法によれば従来硫化水素含有ガスのアルカ
リ処理において欠点とされていた炭酸ソーダ全有効に利
用することができる。また処理液の使用量を得らnるガ
ス吸収液中の硫化ソーダと水硫化ソーダとの比(Na5
N/Na、s)が0.6〜1.2となるようにすること
により効率よく硫化水i′(il−吸収除去することが
できると共に、炭酸ガスによるアルカリ水溶液の消費量
を減少せしめ、経済的にアルカリ処理を行うことができ
る。更にガス吸収液の処理においてもガス吸収液中には
多量の炭酸ソーダが含まれていないから、容易にしかも
経済的に処理することができる等の利点もあり、本発明
方法は硫化水素ガスガス全アルカリ処理によって吸収除
去する方法において極めて顕著な実用的効果を奏する。
As described above, the method of the present invention involves completely absorbing and removing hydrogen sulfide by treating the gas containing hydrogen monosulfide with an alkali aqueous solution using alkali aqueous solution. Since the treatment liquid obtained by treatment with calcium hydroxide is reused for the alkali treatment of gas containing sulfur compounds, the amount of water in the gas absorption liquid is lower than in the conventional case where the entire gas absorption liquid is recycled. The total equilibrium concentration of soda carbonate can be reduced completely, there is no trouble caused by crystals of soda carbonate during alkali treatment, and since the treatment solution contains caustic soda, the amount of new aqueous alkali solution to be added is small. Therefore, alkaline treatment can be carried out stably and economically, and according to the method of the present invention, all of the soda carbonate, which has been considered a drawback in the conventional alkaline treatment of hydrogen sulfide-containing gas, can be fully utilized. Also, the ratio of sodium sulfide to sodium hydrogen sulfide in the gas absorption liquid (Na5
By adjusting N/Na,s) to be 0.6 to 1.2, sulfide water i' (il-) can be efficiently absorbed and removed, and the amount of alkaline aqueous solution consumed by carbon dioxide gas can be reduced. Alkaline treatment can be carried out economically.Furthermore, since the gas absorption liquid does not contain a large amount of soda carbonate, it can be treated easily and economically. Therefore, the method of the present invention has extremely remarkable practical effects in the method of absorbing and removing hydrogen sulfide gas by total alkali treatment.

以下、本発明方法を実施例によって具体的に説明する。Hereinafter, the method of the present invention will be specifically explained using examples.

実施例1 接触反応塔(1210φ×647ワH)に充填物トシて
バイレックス÷300 (商品名、東洋ゴム工業株式会
社製)を高さ3300van充填し、レーヨン紡糸工程
より発生する硫化水素含有ガス(硫化水素ガス濃度60
ppm)を風量1800°−で供給し、一方濃度2ツO
?/1の苛性ソーダ水溶液ヲNa5N/Na、sの比が
O,’7〜0.9になるように供給した。このとき処理
排ガス中の硫化水素ガスの濃度は0.9 ppH1であ
り、ガス吸収液中の硫黄化合物及び炭酸化合物は次の通
りであった。
Example 1 A contact reaction tower (1210φ x 647WH) was packed with Virex ÷ 300 (trade name, manufactured by Toyo Tire & Rubber Industries, Ltd.) to a height of 3300vans, and hydrogen sulfide-containing gas generated from the rayon spinning process was collected. (Hydrogen sulfide gas concentration 60
ppm) at an air volume of 1800°-, while the concentration of 2 O
? An aqueous solution of Na5N/Na,s of 1/1 was supplied so that the ratio of Na5N/Na,s was O,'7 to 0.9. At this time, the concentration of hydrogen sulfide gas in the treated exhaust gas was 0.9 ppH1, and the sulfur compounds and carbonate compounds in the gas absorption liquid were as follows.

Nat S : a59/l、 Na5H: 33 的
、 Na2 co、 : 151 ’/l−り出し、こ
れに濃度2L3%の水酸化カルシウム水溶液35t′(
il−加え、温度95℃で30分間処理してp別し、処
理液901に得た。この処理液の組成は次の通りであっ
た。
NatS: a59/l, Na5H: 33%, Na2co,: 151'/l - was taken out, and to this was added 35t' of calcium hydroxide aqueous solution with a concentration of 2L and 3% (
il- was added thereto, and treated at a temperature of 95° C. for 30 minutes to separate p, yielding treated solution 901. The composition of this treatment liquid was as follows.

NaOH: 4t?/1 、 Na2S : 61r/
z 、 Na2003 : l’7 V/、1この処理
液にガス吸収液全混合し、更に濃度2ツ017、の苛性
ソーダー上顎えて、生成する硫化ソーダと水硫化ソーダ
の比(Na5H/Ha2S )がO,’7〜0゜9、全
硫化ソーダの濃度がl OOP/lになるように供給し
、上記と同様にして硫化水素含有ガス(硫化水素ガス濃
度6oppm)’を処理したところ、処理排ガス中の硫
化水素ガス濃度はl ppmであった。
NaOH: 4t? /1, Na2S: 61r/
z, Na2003: l'7 V/, 1 This treatment liquid is mixed with all the gas absorption liquid, and then added with caustic soda of 2 to 017 concentration, the ratio of sodium sulfide and sodium hydrogen sulfide (Na5H/Ha2S) to be produced is When hydrogen sulfide-containing gas (hydrogen sulfide gas concentration 6 oppm) was supplied in the same manner as above, the total sodium sulfide concentration was 1 OOP/l. The concentration of hydrogen sulfide gas inside was 1 ppm.

このようにして処理液ケ循環使用したところガス吸収液
の濃度は下記の平衡濃度に達した。
When the treatment liquid was circulated and used in this manner, the concentration of the gas absorption liquid reached the equilibrium concentration shown below.

Na、S : 44y/l、 Na5H: 34Y/l
 、 NatOOs: 559/1このように本発明方
法による場合はガス吸収液中には炭酸ソーダが僅かしか
含有されていないため、安定した連続運転が可能であシ
、またガス吸収液全そのまま循環する場合に新しく添加
する苛性ソーダ量15−(純分)に比して本発明方法の
場合はその量が9−(純分)と約40%節減することが
できた。
Na, S: 44y/l, Na5H: 34y/l
, NatOOs: 559/1 As described above, in the case of the method of the present invention, since the gas absorption liquid contains only a small amount of soda carbonate, stable continuous operation is possible, and the entire gas absorption liquid is circulated as it is. Compared to the amount of caustic soda newly added in the case of 15-(purity), in the case of the method of the present invention, the amount was reduced by about 40% to 9-(pure).

一方、前記のようにして循環使用した過剰のガス吸収液
全2倍量の水で稀釈し、ガス発生装置に供給し、反応装
置内の圧力1−0.040〜−0.O15%温度45±
2℃、  PHを5〜6に調整しながら60%の硫酸を
供給して処理した。この場合、硫酸の所要量はガス母収
液をそのまま硫酸処理する場合の所要量に対して約35
%節減することができ、しかも硫酸処理も極めて容易で
あった。
On the other hand, the excess gas absorption liquid circulated as described above was diluted with twice the total amount of water, and supplied to the gas generator, so that the pressure inside the reactor was 1-0.040 to -0. O15% temperature 45±
The treatment was carried out at 2°C by supplying 60% sulfuric acid while adjusting the pH to 5-6. In this case, the required amount of sulfuric acid is approximately 35% of the amount required when directly treating the gas mother liquid with sulfuric acid.
% reduction, and the sulfuric acid treatment was also extremely easy.

また、得られた混合ガス中の炭酸ガス濃度が低いため、
安定した燃焼を行うことができ、この排ガスは通常の排
煙脱硫装置で処理することができたO
In addition, since the carbon dioxide concentration in the obtained mixed gas is low,
Stable combustion can be carried out, and this exhaust gas can be treated with ordinary flue gas desulfurization equipment.

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

図は本発明方法の一例會示すフロー概略図である0 (1)・・・接触反応塔、(2)・・・充填物。 (3)・・・硫化水嚢含有ガス。 (5)・・・苛性ソーダ水溶液、(6)・・処理排ガス
。 (7)・・・ガス吸収液。 (8)・・・ガス吸収液貯蔵タンク。 OC・・・熱交換器、 0ト・・処理槽。 Q21・・・水酸化カルシウム水溶液貯蔵タンク。 041・・・涙過装置、a5)・・・処理液。 06)・・処理液貯蔵タンク。 特許出願人  ユニチカ株式会社
The figure is a flow diagram showing an example of the method of the present invention. (1)...Catalytic reaction tower, (2)... Packing. (3)...Sulfide water sac containing gas. (5)... Caustic soda aqueous solution, (6)... Treated exhaust gas. (7)...Gas absorption liquid. (8)...Gas absorption liquid storage tank. OC...heat exchanger, OC...processing tank. Q21... Calcium hydroxide aqueous solution storage tank. 041...Lacrimal filtration device, a5)...Processing liquid. 06)...Processing liquid storage tank. Patent applicant Unitika Co., Ltd.

Claims (1)

【特許請求の範囲】 l 硫化水素含有ガスをアルカリ水溶液でアルカリ処理
し硫化水素を吸収除去する方法において、前記硫化水素
を吸収したガス吸収液を水酸化カルシウムで処理した後
、p過し、得られた処理液全硫化水素含有ガスのアルカ
リ処理に再使用することを特徴とする硫化水素含有ガス
の処理方法。 ユ ガス吸収液中の硫化ソーダと水硫化ソーダの比が0
.6〜L2になるような量で処理液上アルカリ処理に再
使用する特許請求の範囲第1項記載の硫化水素含有ガス
の処理方法。
[Scope of Claims] l In a method of absorbing and removing hydrogen sulfide by treating hydrogen sulfide-containing gas with an alkaline aqueous solution, the gas absorption liquid that has absorbed hydrogen sulfide is treated with calcium hydroxide, and then subjected to p-filtration. A method for treating a hydrogen sulfide-containing gas, characterized in that the entire treated solution is reused for alkaline treatment of the hydrogen sulfide-containing gas. The ratio of sodium sulfide and sodium hydrogen sulfide in the gas absorption liquid is 0.
.. 6. The method for treating hydrogen sulfide-containing gas according to claim 1, wherein the amount is reused for the alkali treatment on the treatment liquid in an amount of 6 to 2 L2.
JP57086158A 1982-05-20 1982-05-20 Treatment of hydrogen sulfide-containing gas Pending JPS58202021A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57086158A JPS58202021A (en) 1982-05-20 1982-05-20 Treatment of hydrogen sulfide-containing gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57086158A JPS58202021A (en) 1982-05-20 1982-05-20 Treatment of hydrogen sulfide-containing gas

Publications (1)

Publication Number Publication Date
JPS58202021A true JPS58202021A (en) 1983-11-25

Family

ID=13878927

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57086158A Pending JPS58202021A (en) 1982-05-20 1982-05-20 Treatment of hydrogen sulfide-containing gas

Country Status (1)

Country Link
JP (1) JPS58202021A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015039652A (en) * 2013-08-20 2015-03-02 栗田工業株式会社 Method and apparatus for treating selenium-containing water
JP2015039651A (en) * 2013-08-20 2015-03-02 栗田工業株式会社 Method and apparatus for treating selenium-containing water
CN106334413A (en) * 2016-10-19 2017-01-18 成都卓立环保工程有限公司 Method for combined treatment of sulfur-containing exhaust gas and sulfur-containing wastewater

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015039652A (en) * 2013-08-20 2015-03-02 栗田工業株式会社 Method and apparatus for treating selenium-containing water
JP2015039651A (en) * 2013-08-20 2015-03-02 栗田工業株式会社 Method and apparatus for treating selenium-containing water
CN106334413A (en) * 2016-10-19 2017-01-18 成都卓立环保工程有限公司 Method for combined treatment of sulfur-containing exhaust gas and sulfur-containing wastewater

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