JPS5824170B2 - High gas stew - Google Patents
High gas stewInfo
- Publication number
- JPS5824170B2 JPS5824170B2 JP49069718A JP6971874A JPS5824170B2 JP S5824170 B2 JPS5824170 B2 JP S5824170B2 JP 49069718 A JP49069718 A JP 49069718A JP 6971874 A JP6971874 A JP 6971874A JP S5824170 B2 JPS5824170 B2 JP S5824170B2
- Authority
- JP
- Japan
- Prior art keywords
- surfactant
- added
- exhaust gas
- gas
- stew
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
Classifications
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Treating Waste Gases (AREA)
Description
【発明の詳細な説明】
本発明は燃焼炉排ガス中の窒素酸化物(NOx)のよう
に、大部分が一酸化窒素(NO)から成るNOxを湿式
法によって効率よく除去する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for efficiently removing NOx, which consists mostly of nitrogen monoxide (NO), such as nitrogen oxides (NOx) in combustion furnace exhaust gas, by a wet method. .
湿式法においてNOを吸収除去することのできる吸収液
としては、NOと錯塩を形成する硫酸第一鉄および亜硫
酸ナトIJウムの水溶液があること、また亜硫酸ナトリ
ウムはNOを無害な窒素に還元する作用のあることなど
が知られている。Absorbing liquids that can absorb and remove NO in the wet method include aqueous solutions of ferrous sulfate and sodium sulfite, which form complex salts with NO, and sodium sulfite has the effect of reducing NO to harmless nitrogen. It is known that there are
しかし硫酸第一鉄は燃焼炉排ガスのように、通常Noの
100倍以上の高濃度で共存する酸素によって容易に硫
酸第二鉄に酸化されるため、No吸収能力を失って来る
。However, ferrous sulfate is easily oxidized to ferric sulfate by oxygen, which normally coexists at a concentration 100 times higher than that of No, such as combustion furnace exhaust gas, and thus loses its No absorption ability.
また亜硫酸ナトリウムによるNO吸収法あるいはNOの
N2への還元法は、排ガス中のNOxが殆んど除去され
ないことかられかるように反応速度が著しく遅い。Furthermore, in the NO absorption method using sodium sulfite or the reduction method of NO to N2, the reaction rate is extremely slow as almost no NOx in the exhaust gas is removed.
そこで本発明者らは上記の如き従来方法の欠点の除去に
ついて研究したところ、吸収液に水溶性の触媒を添加す
ることにより、上記のNoと亜硫酸ナトリウムとの反応
速度を著しく促進させることができることを見出した。Therefore, the present inventors conducted research on eliminating the drawbacks of the conventional method as described above, and found that by adding a water-soluble catalyst to the absorption liquid, the reaction rate between the above-mentioned No and sodium sulfite can be significantly accelerated. I found out.
また吸収塔としては、充填塔よりも気泡塔の方が高いN
Oχ除去率が得られることを解明した。Also, as an absorption tower, a bubble tower has higher N than a packed tower.
It was clarified that the Ox removal rate could be obtained.
すなわち多数の無機金属塩、有機金属塩、金属錯塩およ
び金属キレート化合物のうちから最も高性能の触媒とし
て選び出した鉄キレート化合物、例えばエチレンジアミ
ン四酢酸、ジヒロドロキシエチルグリシン、エチレンジ
アミンジオルトヒドロキシフェニル酢酸などの第一鉄キ
レートを亜硫酸アルカリ水溶液11につき0.001〜
002モル添加した吸収液に、燃焼炉排ガスのように主
としてNoからなるNOxおよびS02を含有するガス
を流通させる方法である。That is, iron chelate compounds selected as the highest performance catalysts from among a large number of inorganic metal salts, organic metal salts, metal complex salts, and metal chelate compounds, such as ethylenediaminetetraacetic acid, dihydroxyethylglycine, and ethylenediaminediorthohydroxyphenylacetic acid. Ferrous chelates such as 0.001 to 11 per 11 aqueous sulfite
This is a method in which a gas containing mainly NOx and S02, such as combustion furnace exhaust gas, is passed through the absorption liquid to which 0.02 mole is added.
この方法によれば反応速度を著しく促進させながら、N
OxとSO□とを効率よく除去できる。According to this method, N
Ox and SO□ can be removed efficiently.
例えば内径4crI′L、長さ150cmのガラス管内
(こpH6,5〜70に調節した10%亜硫酸ナトリウ
ム水溶液を液柱高さ100Cr/l入れて、液温を50
°Cに温め、下方より挿入したガラスフィルタ(40〜
50ミクロン)付きのガス通気管を通してNO265p
pm、 S O2500ppmを含むNO,S02およ
びN2の混合ガスを毎分1.51の割合で送入した。For example, in a glass tube with an inner diameter of 4crI'L and a length of 150cm, a 10% aqueous sodium sulfite solution adjusted to pH 6.5 to 70 is poured to a liquid column height of 100Cr/L, and the liquid temperature is adjusted to 50cm.
Warm it to °C and insert a glass filter from below (40~
NO265p through gas vent pipe with 50 micron)
A mixed gas of NO, SO2 and N2 containing 500 ppm of SO2 was fed at a rate of 1.51 per minute.
するとガスは内径的8mmの気泡となって吸収液と接触
した。Then, the gas became bubbles with an inner diameter of 8 mm and came into contact with the absorption liquid.
通気による液柱上昇が約20CTしてあったことから、
気泡の液柱内通適時間は約8秒であった。Since the rise in the liquid column due to ventilation was approximately 20CT,
The appropriate time for bubbles to pass through the liquid column was about 8 seconds.
各種の薬品を添加してNo除去率をを比較すると表1の
通りである。Table 1 shows a comparison of the No removal rates after adding various chemicals.
この表で明らかなように、第一鉄および第二鉄キレート
化合物、無機および有機の第一鉄塩などが良好であるが
、混合ガスに酸素ガスを1〜5%添加すると表2に示す
ように第一鉄および第二鉄のキレート化合物以外はいず
れも酸素濃度3%以上になるとNo除去率が低下するこ
とがわかる。As is clear from this table, ferrous and ferric chelate compounds, inorganic and organic ferrous salts, etc. are good, but when 1 to 5% oxygen gas is added to the mixed gas, as shown in Table 2, It can be seen that, except for chelate compounds of ferrous and ferric iron, the No removal rate decreases when the oxygen concentration becomes 3% or more.
本発明は上記の如き本発明者等によって提案された方法
に用いられる吸収液に界面活性剤を添加すると、さらに
顕著にNOχ除去率を向上させうろことを見出してなさ
れたもので、その特徴とするところは吸収液に、界面活
性剤を微量(0,0001〜0.002%)添加して溶
液の表面張力を僅か低下させることによって、気泡塔内
を流通する排ガスつ気泡の大きさを微細化して、NOx
とSO2の除去率を顕著に向上させることにある。The present invention was made based on the discovery that when a surfactant is added to the absorption liquid used in the method proposed by the present inventors as described above, the NOx removal rate can be further significantly improved. By adding a small amount (0,0001 to 0.002%) of a surfactant to the absorption liquid to slightly lower the surface tension of the solution, the size of the exhaust gas bubbles flowing in the bubble column can be reduced. and NOx
and to significantly improve the SO2 removal rate.
本発明において添加する界面活性剤としては、市販のア
ルキルベンゼンスルホン酸ナトリウム、高級アルコール
硫酸エステルナトリウム、アルキル硫酸エステルナトリ
ウムの如き陰イオン系界面活性剤、ヘキサデシルトリメ
チルアンモニウムクロライド、アルキルトリメチルアン
モニウムクロライド、アルキルピリジニウムクロライド
、ジシアミンーシアミン混合物の如き陽イオン系界面活
性剤、ジメチルアルキルベタイン、アルキルベタイン、
アルキルイミダシリンの如き両性系界面活性剤およびH
LBl 4以上のポリオキシエチレンアルキルフェニル
エーテルの如き非イオン系界面活性剤が使用できるが、
そのうちで水溶性でありかつ発泡性の少ないものがよい
。Examples of the surfactant to be added in the present invention include commercially available anionic surfactants such as sodium alkylbenzene sulfonate, sodium higher alcohol sulfate, sodium alkyl sulfate, hexadecyltrimethylammonium chloride, alkyltrimethylammonium chloride, and alkylpyridinium chloride. Cationic surfactants such as chloride, diciamin-cyamine mixtures, dimethylalkylbetaine, alkylbetaine,
Amphoteric surfactants such as alkylimidacillin and H
Nonionic surfactants such as polyoxyethylene alkylphenyl ethers having an LBL of 4 or more can be used, but
Among these, those that are water-soluble and have low foaming properties are preferred.
界面活性剤の添加は塔内を流通する気泡径を小さくして
NOχ除去効果を高めるのであるが、その効果は0.0
001〜0.002%の範囲内が好ましい。Addition of surfactant reduces the diameter of bubbles flowing in the column and increases the NOx removal effect, but the effect is 0.0
It is preferably within the range of 0.001% to 0.002%.
一方界面活性剤の添加量を0.002%以上に増加させ
ると発泡性を増して気泡がガスと共に塔外まで浴出する
ものもある。On the other hand, if the amount of surfactant added is increased to 0.002% or more, foaming properties may be increased and bubbles may be blown out of the tower together with gas.
Noχ除去効果を高め、かつ気泡の発生をなるべく少な
くする界面活性剤の添加量は前述のように0.0001
〜0.002%の範囲がよい。As mentioned above, the amount of surfactant added to enhance the Noχ removal effect and minimize the generation of bubbles is 0.0001.
A range of 0.002% is preferable.
なお上記の界面活性剤を系統別に整理して示すと次の通
りである。The above surfactants are organized by system as follows.
陰イオン系界面活性剤;アルキンベンゼンスルホン酸ナ
トリウム、高級アルコール硫酸エステルナトリウム、ア
ルキル硫酸エステルナトリウム
陽イオン系界面活性剤;ヘキサドデシルI−IJメチル
アンモニウムクロライド、アルキルトリメチルアンモニ
ウムクロライド、ジシアミンーシアミン混合物、アルキ
ルベクイン
両性系界面活性剤;ジメチルアルキルベタイン、アルキ
ルイミダシリン
非イオン系界面活性剤;ポリオキシエチレンアルキルエ
ーテル
本発明について実施例を挙げて具体的に説明する。Anionic surfactant: Sodium alkynebenzene sulfonate, sodium higher alcohol sulfate, sodium alkyl sulfate Cationic surfactant: Hexadodecyl I-IJ methylammonium chloride, alkyltrimethylammonium chloride, diciamine-cyamine mixture , alkylbequin amphoteric surfactant; dimethylalkylbetaine, alkylimidacillin nonionic surfactant; polyoxyethylene alkyl ether The present invention will be specifically explained with reference to Examples.
内径4CrIL1長さ150cmのガラス管内に、10
%の亜硫酸ナトリウム水溶液にエチレンジアミン四酢酸
第−鉄を0.01モル/l添加したものを、液柱高さ2
5C′rI′Lで入れて液温を50°Cに温め、下方よ
り挿入したガラスフィルタ(40〜50ミクロン)付き
のガス通気管を通して、NO265ppm、5O250
0p障を含むNo 、SO2およびN2の混合ガスを毎
分1.51の割合で流通させたとき、N。In a glass tube with an inner diameter of 4 CrIL and a length of 150 cm, 10
% sodium sulfite aqueous solution to which 0.01 mol/l of ferrous ethylenediaminetetraacetate was added, and the liquid column height was 2.
5C'rI'L was added to warm the liquid temperature to 50°C, and it was passed through a gas ventilation tube with a glass filter (40 to 50 microns) inserted from below to produce NO265ppm and 5O250.
When a mixed gas of No 2 , SO 2 and N 2 containing 0p impediment is passed at a rate of 1.51 per minute, N.
除去率は75%あった。The removal rate was 75%.
し7かしこの吸収液に界面活性剤を微量添加してNOχ
除去効果を比較すると表3に示す通りとなり、界面活性
剤がNo除去率を顕著に向上させる効果を有することが
わかる。However, by adding a small amount of surfactant to this absorption liquid, NOχ
A comparison of the removal effects is as shown in Table 3, which shows that the surfactant has the effect of significantly improving the No removal rate.
Claims (1)
液11につき0.001〜0.02モル添加した吸収液
に、界面活性剤を微量すなわち0.0001〜0.00
2%添加した後燃焼炉排ガスを流通することを特徴とす
る排ガス中の窒素酸化物および亜硫酸ガスの除去方法。1. A trace amount of a surfactant, that is, 0.0001 to 0.00, is added to an absorption liquid in which 0.001 to 0.02 mole of an iron chelate compound is added per 11 of the aqueous solution to an aqueous solution of alkali sulfite.
A method for removing nitrogen oxides and sulfur dioxide gas from exhaust gas, which comprises circulating post-combustion furnace exhaust gas containing 2% additive.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP49069718A JPS5824170B2 (en) | 1974-06-20 | 1974-06-20 | High gas stew |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP49069718A JPS5824170B2 (en) | 1974-06-20 | 1974-06-20 | High gas stew |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS50160167A JPS50160167A (en) | 1975-12-25 |
| JPS5824170B2 true JPS5824170B2 (en) | 1983-05-19 |
Family
ID=13410879
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP49069718A Expired JPS5824170B2 (en) | 1974-06-20 | 1974-06-20 | High gas stew |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5824170B2 (en) |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5096478A (en) * | 1973-12-27 | 1975-07-31 | ||
| JPS50102588A (en) * | 1974-01-17 | 1975-08-13 |
-
1974
- 1974-06-20 JP JP49069718A patent/JPS5824170B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS50160167A (en) | 1975-12-25 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US4035470A (en) | Process for removing sulfur oxides and/or nitrogen oxides from waste gas | |
| US3957949A (en) | Process for removing nitrogen oxides from gas | |
| US3984522A (en) | Method of removing nitrogen monoxide from a nitrogen monoxide-containing gas | |
| Andrew et al. | D1. The dynamics of nitrous gas absorption | |
| US4061743A (en) | Exhaust gas scrubbing process | |
| ES2337996T3 (en) | PROCEDURE TO REDUCE NOX CONTENT IN RESIDUAL GAS CURRENTS USING CHLORINE DIOXIDE. | |
| JPH11347357A (en) | Removal of nox and sox from gaseous effluent from metal pickling bath | |
| US6872371B2 (en) | Method and apparatus for NOx and SO2 removal | |
| US4081509A (en) | Method for removing nitrogen oxides from flue gas by absorption | |
| CA1180538A (en) | Removal of co.sub.2 from gas mixtures | |
| JPS5824170B2 (en) | High gas stew | |
| US4387037A (en) | Removal of sulfur from waste gas streams | |
| CA2525610C (en) | A catalytic composition for oxidation-reduction process for effecting the catalytic oxidation of hydrogen sulfide in gas streams | |
| JPS6134853B2 (en) | ||
| JPH02277522A (en) | Process for removing sox from gas mixture | |
| KR100401996B1 (en) | Improved method of wet scrubbing of nitrogen oxides from flue gas | |
| KR20220139664A (en) | DMPS synthesis method for reducing NOx, SOx in fuel gas | |
| CA1151848A (en) | Removal of sulfur from waste gas streams | |
| JP3649426B2 (en) | How to clean harmful gases | |
| JPS598165B2 (en) | How to remove nitrogen oxides | |
| JPH02203921A (en) | Wet method for removing nitrogen oxides from various combustion exhaust gases | |
| JPH02229527A (en) | Method for simultaneous removal of sulfur oxides and nitrogen oxides | |
| SU1139700A1 (en) | Method of obtaining bromine | |
| US4234548A (en) | Control of nitrogen oxides from stationary source effluents | |
| JPS6388024A (en) | Removal of mercury in exhaust gas |