JPS62186925A - Treatment of exhaust gas - Google Patents
Treatment of exhaust gasInfo
- Publication number
- JPS62186925A JPS62186925A JP61027998A JP2799886A JPS62186925A JP S62186925 A JPS62186925 A JP S62186925A JP 61027998 A JP61027998 A JP 61027998A JP 2799886 A JP2799886 A JP 2799886A JP S62186925 A JPS62186925 A JP S62186925A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- gas
- mercury
- acidic
- neutralizing agent
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000000843 powder Substances 0.000 claims abstract description 18
- 230000002378 acidificating effect Effects 0.000 claims abstract description 15
- 230000003472 neutralizing effect Effects 0.000 claims abstract description 9
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 claims description 28
- 229910052753 mercury Inorganic materials 0.000 claims description 28
- 238000000034 method Methods 0.000 claims description 13
- 150000003464 sulfur compounds Chemical class 0.000 claims description 5
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 4
- 229910052717 sulfur Inorganic materials 0.000 claims description 4
- 239000011593 sulfur Substances 0.000 claims description 4
- QXKXDIKCIPXUPL-UHFFFAOYSA-N sulfanylidenemercury Chemical compound [Hg]=S QXKXDIKCIPXUPL-UHFFFAOYSA-N 0.000 claims description 2
- 239000000376 reactant Substances 0.000 abstract description 14
- 239000003795 chemical substances by application Substances 0.000 abstract description 11
- 238000002485 combustion reaction Methods 0.000 abstract description 8
- 239000012717 electrostatic precipitator Substances 0.000 abstract description 5
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 abstract description 4
- 239000000920 calcium hydroxide Substances 0.000 abstract description 4
- 235000011116 calcium hydroxide Nutrition 0.000 abstract description 4
- 229910001861 calcium hydroxide Inorganic materials 0.000 abstract description 4
- 239000000428 dust Substances 0.000 abstract description 4
- 239000002956 ash Substances 0.000 abstract description 3
- 239000004071 soot Substances 0.000 abstract description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 abstract 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract 2
- 239000007789 gas Substances 0.000 description 51
- 239000002253 acid Substances 0.000 description 13
- 150000002731 mercury compounds Chemical class 0.000 description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 5
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 5
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 5
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 229910052815 sulfur oxide Inorganic materials 0.000 description 3
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-N carbonic acid Chemical compound OC(O)=O BVKZGUZCCUSVTD-UHFFFAOYSA-N 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000010574 gas phase reaction Methods 0.000 description 1
- 239000010800 human waste Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 101150115538 nero gene Proteins 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 235000011121 sodium hydroxide Nutrition 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は都市ごみ焼却炉、産廃焼却炉、し尿・下水汚泥
焼却炉等の排ガス処理装置に適用することができる乾式
排ガス処理方法に関し、特に、排ガス中の水銀成分と酸
性ガス成分とを除去するだめの処理方法に関する。[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a dry exhaust gas treatment method that can be applied to exhaust gas treatment equipment such as municipal waste incinerators, industrial waste incinerators, human waste/sewage sludge incinerators, etc. , relates to a waste treatment method for removing mercury components and acid gas components from exhaust gas.
従来、燃焼排ガス中の水銀及び水銀化合物と酸性ガスを
同時に除去する方法としては、湿式除去法だけが知られ
ており、本発明のように乾式法はなかった。湿式除去法
とは、カセイソーダ水溶液、炭酸力〜シウム又は消石灰
スラリー溶液を用い、気液接触によりガス中の水銀と酸
性ガスを液側へ移行させるものであった。Conventionally, only a wet removal method has been known as a method for simultaneously removing mercury, mercury compounds, and acid gas from combustion exhaust gas, and there has been no dry method as in the present invention. The wet removal method uses a caustic soda aqueous solution, carbonic acid or slaked lime slurry solution, and transfers mercury and acid gas in the gas to the liquid side through gas-liquid contact.
従来の湿式除去法では、水銀を含有する排水の処理が必
要となシ設備が繁雑になるとの欠点があった。従って、
乾式法で水銀が除去でき、且つ酸性ガスが同時に除去で
きるならば、排水処理の懸案が解決できまた同一システ
ムで水銀と酸性ガスが処理でき効果は大きいものと期待
された。The conventional wet removal method has the disadvantage that it requires complicated equipment to treat wastewater containing mercury. Therefore,
If mercury could be removed using a dry method, and acid gases could be removed at the same time, it was expected that the problems of wastewater treatment would be resolved, and that mercury and acid gases could be treated in the same system, which would be highly effective.
本発明は従来の、水銀及び酸性ガスを含有する排ガス処
理方法の欠点を解消し、乾式法によシ水銀と酸性ガスと
を同時処理を可能とし、かつ、処理粉末を電気集じん器
等で容易に除去可能とした排ガス処理方法を提供しよう
とするものである。The present invention eliminates the drawbacks of conventional exhaust gas treatment methods containing mercury and acidic gases, makes it possible to simultaneously treat mercury and acidic gases by a dry method, and uses the treated powder in an electrostatic precipitator or the like. The purpose is to provide a method for treating exhaust gas that can be easily removed.
本発明は排ガス中に、硫黄または水不溶性硫黄化合物と
酸性ガス中和剤を粉体状で噴射し、排ガス中の水銀成分
を化学的に安定な硫化水銀の粉末とし、かつ、排ガス中
の酸性ガスを酸性ガス中和剤で中和して除去することを
特徴とする排ガスの処理方法である。The present invention injects sulfur or a water-insoluble sulfur compound and an acid gas neutralizer in powder form into exhaust gas, converts the mercury component in the exhaust gas into chemically stable mercury sulfide powder, and This is an exhaust gas treatment method characterized by neutralizing and removing gas with an acidic gas neutralizer.
なお、水不溶性硫黄化合物としてはFeS。Note that the water-insoluble sulfur compound is FeS.
ZnS、 Cab、 Cue 等の粉末を用いること
ができる。これらの硫黄または水不溶性硫黄化合物から
なる水銀反応剤と排ガス中の水銀及び水銀化合物との反
応は固気相反応であるので、反応を促進させるためには
反応剤粒子の表面積を大きくし、即ち、粒子を極力小さ
くする必要がある。Powder of ZnS, Cab, Cue, etc. can be used. Since the reaction between these mercury reactants made of sulfur or water-insoluble sulfur compounds and mercury and mercury compounds in exhaust gas is a solid-gas phase reaction, in order to accelerate the reaction, the surface area of the reactant particles must be increased, i.e. , it is necessary to make the particles as small as possible.
しかし、反応剤は煙道に噴霧して気流に乗せる必要があ
り、また、電気集じん器等で捕集する必要があるところ
から、反応剤の粒度は10〜300メツシユ、好ましく
は200〜300メツシユの範囲である。However, the particle size of the reactant is 10 to 300 mesh, preferably 200 to 300 mesh, because the reactant needs to be sprayed into the flue and carried by the airflow, and it needs to be collected by an electrostatic precipitator or the like. This is the range of Metsuyu.
また、酸性ガス中和剤は力μシウム、又はマグネシウム
の水酸化物、炭酸塩、酸化物などを用いることができる
。Further, as the acidic gas neutralizing agent, hydroxide, carbonate, oxide, etc. of μsium or magnesium can be used.
粉体の噴射量は水銀反応剤について排ガス量当り0.1
〜10 jj/Nm” 、中和剤にっ1ハては1〜10
g/N@3が好ましい。The injection amount of powder is 0.1 per exhaust gas amount for mercury reactant.
~10 jj/Nm", 1 to 10 for neutralizing agent
g/N@3 is preferred.
水銀反応剤と中和剤を煙道中に噴射するときに各々個別
的に行なうこともでき、また、2種の粉体を予じめ混合
して同じノズpがら噴射することもできる。The mercury reactant and the neutralizer can be injected into the flue individually, or the two types of powder can be mixed in advance and injected from the same nozzle.
反応温度については、通常の燃焼排ガスの露点が100
〜120℃以上であり、それ以下では結露を生じて反応
剤に濡れ現象を起し、反応剤が固着、付着が生じノズル
の閉塞するなどの不都合が生ずるので、120℃で操作
する必要がある。また、高温で熱分解を起すので、12
0〜400℃の範囲で反応を行なうことが好ましい。Regarding the reaction temperature, the dew point of normal combustion exhaust gas is 100
It is necessary to operate at 120℃ or higher, as if the temperature is lower than that, dew condensation will occur and the reactant will become wet, causing problems such as the reactant sticking or sticking and clogging the nozzle. . In addition, thermal decomposition occurs at high temperatures, so 12
It is preferable to carry out the reaction at a temperature in the range of 0 to 400°C.
第1図は本発明を実施するだめの装置の構成図である。 FIG. 1 is a block diagram of an apparatus for carrying out the present invention.
燃焼排ガス発生源1で発生した水銀及び水銀化合物と酸
性ガス(例えば塩化水素、硫黄酸化物など)を含む燃焼
排ガス中に、1!L気゛集じん器3のガス流れ前方の排
ガスダクト2中に、粉体供給ノズ/L’6.6’によっ
て、水銀反応剤と酸性ガス中和剤を噴射する。水銀反応
剤と中和剤は粉体サイロ7.7′に貯蔵されており、粉
体定量供給機8,8′で供給量を調節して前記粉体供給
ノズpに送るようになっている。また、このノズルの位
置は前後いずれでもよい。排ガス中に噴射された各粉体
のうち、水銀反応剤は迅速に排ガス中の水銀及び水銀化
合物と反応し、水銀をガス側から粉体側へ固定する一方
、酸性ガス中和剤は排ガス中の酸性ガス(例えば、塩化
水素、硫黄酸化物)と反応して、酸性ガスをガス側から
粉体側へ固定する。In the combustion exhaust gas containing mercury and mercury compounds and acid gases (e.g. hydrogen chloride, sulfur oxides, etc.) generated at the combustion exhaust gas source 1, 1! A mercury reactant and an acidic gas neutralizer are injected into the exhaust gas duct 2 in front of the gas flow of the L-air dust collector 3 by a powder supply nozzle/L'6.6'. The mercury reactant and the neutralizing agent are stored in a powder silo 7, 7', and the supply amount is adjusted by powder metering feeders 8, 8' and sent to the powder supply nozzle p. . Moreover, the position of this nozzle may be either the front or the rear. Among the powders injected into the exhaust gas, the mercury reactant quickly reacts with mercury and mercury compounds in the exhaust gas, fixing mercury from the gas side to the powder side, while the acid gas neutralizer reacts with the mercury and mercury compounds in the exhaust gas, while the acid gas neutralizer reacts with acidic gas (e.g., hydrogen chloride, sulfur oxide) to fix the acidic gas from the gas side to the powder side.
水銀を固定した水銀反応剤と酸性ガスを中和し固定した
中和剤は、排ガス流れ後方の電気集じん器3において、
燃焼排ガス中のばいじんと一緒に捕集され、捕集灰10
として系外へ排出される。そして、水銀と酸性ガスを除
かれた排ガスはクリーンなガスとなって排気ファン4を
経由して煙突5より放出される。The mercury reactant that fixed mercury and the neutralizing agent that neutralized and fixed acidic gas are placed in the electrostatic precipitator 3 at the rear of the exhaust gas flow.
Collected together with soot and dust in combustion exhaust gas, collected ash10
is discharged from the system as The exhaust gas from which mercury and acid gas have been removed becomes clean gas and is discharged from the chimney 5 via the exhaust fan 4.
第1図の装置を用いて次の実験を行なった。 The following experiment was conducted using the apparatus shown in FIG.
塩化水素700ppm、硫黄酸化物50 ppm 。Hydrogen chloride 700ppm, sulfur oxide 50ppm.
水銀及び水銀化合物をl 511q/Nm”含む200
〜250℃の排ガス中に、酸性ガス中ネロ剤として32
5メツシュバス96%の消石灰t−5g/N 7FL
8、水銀反応剤として200〜500メツシュパス95
%のZnSを19/N1rL4 噴射した。200 containing mercury and mercury compounds
32 as a Nero agent in acid gas in exhaust gas at ~250℃
5 mesh bath 96% slaked lime t-5g/N 7FL
8. 200-500 mesh pass 95 as mercury reactant
% ZnS was injected at 19/N1rL4.
その結果、排ガス中の塩化水素、硫黄酸化物及び水銀a
mはそれぞれ140ppm、35ppm、Q、 121
1197NrIL” と低Mすることかで!、当初ノ濃
度に対して、それぞれ80.30及び60%除去できた
。As a result, hydrogen chloride, sulfur oxides and mercury a in exhaust gas
m is 140ppm, 35ppm, Q, 121 respectively
By reducing M to 1197NrIL, we were able to remove 80.30% and 60% of the initial concentration, respectively.
本発明は燃焼排ガス中の煙道に、硫黄または硫黄化合物
と消石灰又は類似の酸性ガス中和剤を粉体状で噴射する
ことにより、排ガス中の塩化水素や硫黄酸化物などの酸
性ガス及び水銀及び水銀化合物を捕集灰として電気集じ
ん器で簡単に除去することができ、燃焼排ガスを効果的
に浄化できる。The present invention eliminates acid gases such as hydrogen chloride and sulfur oxides and mercury in the flue gas by injecting sulfur or sulfur compounds and slaked lime or similar acid gas neutralizer in powder form into the flue in the flue gas. and mercury compounds can be easily removed as collected ash using an electrostatic precipitator, and combustion exhaust gas can be effectively purified.
第1図は、本発明を実施するだめの装置の構成図である
。
復代理人 内 1) 明
復代理人 萩 原 亮 −
復代理人 安 西 篤 夫FIG. 1 is a block diagram of an apparatus for carrying out the present invention. Sub-Agents 1) Meifuku Agent Ryo Hagiwara − Sub-Agent Atsuo Anzai
Claims (1)
中和剤を粉体状で噴射し、排ガス中の水銀成分を化学的
に安定な硫化水銀の粉末とし、かつ、排ガス中の酸性ガ
スを酸性ガス中和剤で中和して除去することを特徴とす
る排ガスの処理方法。Sulfur or a water-insoluble sulfur compound and an acidic gas neutralizer are injected into the exhaust gas in powder form to convert the mercury component in the exhaust gas into chemically stable mercury sulfide powder, and to make the acidic gas in the exhaust gas acidic. A method for treating exhaust gas, characterized by neutralizing and removing it with a gas neutralizer.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP61027998A JPS62186925A (en) | 1986-02-13 | 1986-02-13 | Treatment of exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP61027998A JPS62186925A (en) | 1986-02-13 | 1986-02-13 | Treatment of exhaust gas |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS62186925A true JPS62186925A (en) | 1987-08-15 |
JPH0569569B2 JPH0569569B2 (en) | 1993-10-01 |
Family
ID=12236488
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP61027998A Granted JPS62186925A (en) | 1986-02-13 | 1986-02-13 | Treatment of exhaust gas |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS62186925A (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH03502125A (en) * | 1988-10-27 | 1991-05-16 | サンドストランド・コーポレーション | Sustained propulsion device |
JPH04330917A (en) * | 1991-05-01 | 1992-11-18 | Kubota Corp | Dust collecting method of waste gas |
US5209912A (en) * | 1990-05-02 | 1993-05-11 | Ftu Gmbh | Process for separating out noxious substances from gases and exhaust gases |
WO1997012662A1 (en) * | 1995-10-06 | 1997-04-10 | Kaneka Corporation | Waste gas and dust treatment method |
US6503470B1 (en) * | 1999-03-31 | 2003-01-07 | The Babcock & Wilcox Company | Use of sulfide-containing liquors for removing mercury from flue gases |
US6855859B2 (en) | 1999-03-31 | 2005-02-15 | The Babcock & Wilcox Company | Method for controlling elemental mercury emissions |
CN108889110A (en) * | 2018-08-08 | 2018-11-27 | 中国恩菲工程技术有限公司 | The method for removing hydrargyrum of flue gas |
-
1986
- 1986-02-13 JP JP61027998A patent/JPS62186925A/en active Granted
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH03502125A (en) * | 1988-10-27 | 1991-05-16 | サンドストランド・コーポレーション | Sustained propulsion device |
US5209912A (en) * | 1990-05-02 | 1993-05-11 | Ftu Gmbh | Process for separating out noxious substances from gases and exhaust gases |
JPH04330917A (en) * | 1991-05-01 | 1992-11-18 | Kubota Corp | Dust collecting method of waste gas |
WO1997012662A1 (en) * | 1995-10-06 | 1997-04-10 | Kaneka Corporation | Waste gas and dust treatment method |
US6503470B1 (en) * | 1999-03-31 | 2003-01-07 | The Babcock & Wilcox Company | Use of sulfide-containing liquors for removing mercury from flue gases |
US6855859B2 (en) | 1999-03-31 | 2005-02-15 | The Babcock & Wilcox Company | Method for controlling elemental mercury emissions |
CN108889110A (en) * | 2018-08-08 | 2018-11-27 | 中国恩菲工程技术有限公司 | The method for removing hydrargyrum of flue gas |
Also Published As
Publication number | Publication date |
---|---|
JPH0569569B2 (en) | 1993-10-01 |
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