JP2002001042A - Wet dust collecting method for exhaust gas - Google Patents

Wet dust collecting method for exhaust gas

Info

Publication number
JP2002001042A
JP2002001042A JP2000182477A JP2000182477A JP2002001042A JP 2002001042 A JP2002001042 A JP 2002001042A JP 2000182477 A JP2000182477 A JP 2000182477A JP 2000182477 A JP2000182477 A JP 2000182477A JP 2002001042 A JP2002001042 A JP 2002001042A
Authority
JP
Japan
Prior art keywords
dust
exhaust gas
aqueous solution
surfactant
wet
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
JP2000182477A
Other languages
Japanese (ja)
Inventor
Yasunobu Minamino
康信 南野
Kazuhiro Akaike
一宏 赤池
Hitoshi Ito
仁志 伊藤
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.)
Mitsubishi Kakoki Kaisha Ltd
Original Assignee
Mitsubishi Kakoki Kaisha 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 Mitsubishi Kakoki Kaisha Ltd filed Critical Mitsubishi Kakoki Kaisha Ltd
Priority to JP2000182477A priority Critical patent/JP2002001042A/en
Publication of JP2002001042A publication Critical patent/JP2002001042A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide a wet dust collecting method by which it is possible to capture dust efficiently from an exhaust gas containing the dust at a low installation cost, and especially remove even the dust with low wetting properties such as unburnt carbon or an unburnt oil content present in the exhaust gas discharged from a diesel engine to an aqueous solution, at a high uptake efficiency, and further, by which it is possible to easily treat the captured dust after its uptake process. SOLUTION: In the wet dust collecting method by which the dust present in the exhaust gas containing the dust is brought into contact with the aqueous solution to capture the dust, a surfactant and if necessary, a defoaming agent are added to the aqueous solution and this mixture is used to capture the dust from the exhaust gas.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、ダストを含有する
排ガス中のダストを水溶液と接触させて捕集する湿式除
塵方法に関し、特に、未燃焼カ−ボンや未燃焼油分など
のダストを含有するディ−ゼル発電設備などのディ−ゼ
ル機関から排出される排ガス中のダストを除去するのに
適した湿式除塵方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wet dust removing method for collecting dust in exhaust gas containing dust by bringing the dust into contact with an aqueous solution, and in particular, contains dust such as unburned carbon and unburned oil. The present invention relates to a wet dust removal method suitable for removing dust in exhaust gas discharged from a diesel engine such as a diesel power generation facility.

【0002】[0002]

【従来の技術】従来、ダストを含有する排ガス中のダス
トを除去する除塵方法としては、セラミックスフィルタ
法、エリミネ−タ法、水溶液噴霧法及び水溶液接触法な
どが用いられている。
2. Description of the Related Art Heretofore, as a dust removing method for removing dust in exhaust gas containing dust, a ceramic filter method, an eliminator method, an aqueous solution spraying method, an aqueous solution contacting method, and the like have been used.

【0003】前記セラミックスフィルタ法は、煙道にセ
ラミックス製多孔質フィルタを設置してダストを濾過捕
集し、更に、フィルタを加熱することにより、捕集した
未燃焼カ−ボンや未燃焼油分などのダストを燃焼除去す
る方法であり、粒径の比較的大きなダストの除去には効
果的な方法である。また、前記エリミネ−タ法は、プラ
スチックなどでジグザグ流路を形成したエリミネ−タ
を、排煙脱硫装置の塔頂部や後段に配置してダストを付
着捕集して除去する方法であり、主に排ガス中のミスト
を除去するのに適しており、ダストを副次的に除去する
方法である。また、前記水溶液噴霧法は、排ガス中に水
や排煙脱硫用吸収液をスプレ−ノズルから噴霧させ、ダ
ストをその液粒子中に捕集する方法であり、また、水溶
液接触法は、排ガスを水層と接触させ、ダストをその水
層中に捕集する方法である。
In the above ceramics filter method, a ceramics porous filter is installed in a flue to filter and collect dust, and further, the filter is heated to collect collected unburned carbon and unburned oil. This is an effective method for removing dust having a relatively large particle size. In addition, the eliminator method is a method in which an eliminator having a zigzag flow path formed of plastic or the like is disposed at the top of a flue gas desulfurization unit or at a later stage to adhere and collect dust and remove the dust. This method is suitable for removing mist in exhaust gas, and is a method for removing dust secondarily. In addition, the aqueous solution spraying method is a method in which water or flue gas desulfurization absorbent is sprayed into exhaust gas from a spray nozzle, and dust is collected in liquid particles thereof. In this method, dust is collected in the water layer by contact with the water layer.

【0004】[0004]

【発明が解決しようとする課題】前記従来の排ガスの除
塵方法において、セラミックスフィルタ法では、数μm
以下の粒径の小さなダスト、例えば、ディ−ゼル機関か
ら排出される排ガス中の未燃焼カ−ボンなどの捕集効率
が低く、ダスト量が多い場合にはフィルタが目詰まりを
起こしやすいため適用するのは好ましくなく、また、加
熱するためのエネルギ−コストや設備費が嵩む問題もあ
る。
In the above-mentioned conventional method for removing dust from exhaust gas, the ceramic filter method uses several μm.
Dust having the following small particle size, such as unburned carbon in exhaust gas discharged from diesel engines, has low collection efficiency, and if the amount of dust is large, the filter is likely to be clogged. However, there is also a problem that the energy cost and equipment cost for heating are increased.

【0005】エリミネ−タ法では、ダストは副次的に捕
集される程度であるため捕集効率が低く、また、ディ−
ゼル機関から排出される排ガス中の未燃焼油分などが捕
集され、プラスチック表面に付着する場合などには、そ
れを取り除く的確な方法がないため、人手で洗浄除去す
る煩雑さがあり、蓄積したままにしておくと、処理後の
排ガス中にスリップする恐れがあり、また、設備費が嵩
む問題もある。
[0005] In the eliminator method, dust is only collected as a by-product, so that the dust collection efficiency is low.
When unburned oil in exhaust gas discharged from diesel engines is collected and adheres to the surface of plastics, etc., there is no accurate method to remove it, so there is the trouble of manually cleaning and removing the accumulated oil. If left as it is, there is a risk of slipping in the exhaust gas after treatment, and there is also a problem that the equipment cost increases.

【0006】水溶液噴霧法及び水溶液接触法などの湿式
除塵方法では、水溶液に対して濡れ性がよいダストにつ
いては捕集効率が高いが、ディ−ゼル機関から排出され
る排ガス中の未燃焼カ−ボンや未燃焼油分などの水溶液
に対して濡れ性が低いダストでは、捕集効率が低い問題
がある。
In wet dust removal methods such as an aqueous solution spray method and an aqueous solution contact method, dust having good wettability to an aqueous solution has a high collection efficiency, but unburned dust in exhaust gas discharged from a diesel engine. Dust having low wettability with respect to an aqueous solution such as bon or unburned oil has a problem of low collection efficiency.

【0007】本発明は、前記の問題に鑑みてなされたも
のであり、廉価な設備費でダストを含有する排ガス中の
ダストを効率よく捕集することができ、特に、ディ−ゼ
ル機関から排出される排ガス中の未燃焼カ−ボンや未燃
焼油分などの、水溶液に対して濡れ性が低いダストでも
高い捕集効率で除去することができると共に、捕集後の
処理も容易な湿式除塵方法を提供する目的で成されたも
のである。
The present invention has been made in view of the above-mentioned problems, and can efficiently collect dust in exhaust gas containing dust at a low cost of equipment, and in particular, discharges dust from diesel engines. Wet dust removal method that can remove dust with low wettability to aqueous solution, such as unburned carbon and unburned oil in exhaust gas, with high collection efficiency and easy treatment after collection The purpose was to provide.

【0008】[0008]

【課題を解決するための手段】前記目的を達成するため
の本発明の要旨は、請求項1に記載の発明においては、
ダストを含有する排ガス中のダストを水溶液と接触させ
て捕集する湿式除塵方法において、水溶液に界面活性剤
を添加したことを特徴とする排ガスの湿式除塵方法であ
り、この構成により、水溶液に対して濡れ性が低いダス
トの濡れ性が界面活性剤の作用で改善され、水溶液に捕
集されやすくなる。
The gist of the present invention for achieving the above object is as follows.
In a wet dust removal method of contacting and collecting dust in exhaust gas containing dust with an aqueous solution, the wet dust removal method for exhaust gas is characterized by adding a surfactant to the aqueous solution. The wettability of dust having low wettability is improved by the action of the surfactant, and the dust is easily collected in an aqueous solution.

【0009】また、請求項2に記載の発明においては、
ダストを含有する排ガス中のダストを水溶液と接触させ
て捕集する湿式除塵方法において、水溶液に界面活性剤
及び消泡剤を添加したことを特徴とする排ガスの湿式除
塵方法である。この構成により、ダストの濡れ性が改善
されると共に、捕集時などにおける発泡を抑制すること
ができる。
Further, in the invention according to claim 2,
A wet dust removal method for exhaust gas containing dust, wherein a dust and a defoaming agent are added to an aqueous solution in a wet dust removal method for collecting dust by contacting the dust with an aqueous solution. With this configuration, the wettability of dust is improved, and foaming at the time of collection or the like can be suppressed.

【0010】また、請求項3に記載の発明においては、
請求項1又は請求項2記載の排ガスの湿式除塵方法にお
いて、ダストを含有する排ガスがディ−ゼル機関から排
出される排ガスであり、本発明の湿式除塵方法を、未燃
焼カ−ボンや未燃焼油分などの水溶液に対して濡れ性が
低いダストを多く含有するディ−ゼル機関から排出され
る排ガスに適用することにより、その効果を有効に発揮
することができる。
Further, in the invention according to claim 3,
In the method for wet dust removal of exhaust gas according to claim 1 or 2, the exhaust gas containing dust is exhaust gas discharged from a diesel engine. By applying the present invention to exhaust gas discharged from a diesel engine containing a large amount of dust having low wettability with respect to an aqueous solution such as an oil component, the effect can be effectively exhibited.

【0011】また、請求項4に記載の発明においては、
請求項1〜請求項3のいずれか1項記載の排ガスの湿式
除塵方法において、水溶液が排ガス中の硫黄酸化物を除
去する脱硫吸収液であり、これにより、排煙脱硫装置が
設けられた設備において、特に捕集設備を設ける必要が
ないため、設備費が低廉となる。
Further, in the invention according to claim 4,
4. The method according to claim 1, wherein the aqueous solution is a desulfurization absorbing solution for removing sulfur oxides in the exhaust gas, and the facility is provided with a flue gas desulfurization device. In this case, since it is not necessary to particularly provide a collection facility, the facility cost is reduced.

【0012】[0012]

【発明の実施の形態】本発明の実施の形態を図面に基づ
いて説明する。図1は本発明の一実施の形態の排ガスの
湿式除塵方法を適用した排煙脱硫装置の系統図である。
Embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a system diagram of a flue gas desulfurization apparatus to which a wet dust removal method for exhaust gas according to an embodiment of the present invention is applied.

【0013】符号1は内部に充填床2が形成された充填
床式の脱硫塔であり、塔底部には液溜り槽4、塔頂部に
は処理ガスの排出煙道5が配設されており、充填床2の
上方には、主にミストを分離するエリミネ−タ3が設け
られている。また、充填床2の下方には被処理ガスの導
入口aが接続され、充填床2とエリミネ−タ3との間に
は、充填床2上に脱硫吸収液を供給する吸収液供給管d
が接続され、図示しないが、吸収液を充填床2上に均一
散布する噴霧ノズルが設けられている。
Reference numeral 1 denotes a packed bed type desulfurization column having a packed bed 2 formed therein. A liquid storage tank 4 is provided at the bottom of the tower, and a treatment gas discharge flue 5 is provided at the top of the tower. Above the packed bed 2, an eliminator 3 for mainly separating mist is provided. An inlet a for the gas to be treated is connected below the packed bed 2, and between the packed bed 2 and the eliminator 3, an absorption liquid supply pipe d for supplying a desulfurization absorption liquid onto the packed bed 2.
Although not shown, a spray nozzle for uniformly spraying the absorbing liquid on the packed bed 2 is provided.

【0014】なお、本発明の湿式除塵方法を適用する装
置としては、上記の構成には限定されない。脱硫塔が、
充填床式ではなく、スプレ−式、液膜式及び多孔板式な
ど適宜方式の脱硫塔であってもよく、また、脱硫塔では
なく脱硝塔でもよく、それらとは別配置された除塵塔で
あってもよい。
The apparatus to which the wet dust removal method of the present invention is applied is not limited to the above configuration. The desulfurization tower
Instead of a packed bed type, a desulfurization tower of an appropriate type such as a spray type, a liquid film type, or a perforated plate type may be used, and a denitrification tower may be used instead of a desulfurization tower. You may.

【0015】符号6は吸収液タンク、符号7は界面活性
剤タンク、また、符号8は消泡剤タンクである。なお、
使用する界面活性剤の種類や発泡が少ないダストの除塵
などでは、消泡剤タンク8は特に設ける必要がない。ま
た、脱硫塔ではなく独立した除塵塔などにおいては、吸
収液タンク6は工業用水などの水タンクとなるのは当然
である。
Reference numeral 6 denotes an absorbent tank, reference numeral 7 denotes a surfactant tank, and reference numeral 8 denotes an antifoaming tank. In addition,
The defoaming agent tank 8 does not need to be provided particularly for the type of surfactant used and dust removal with little foaming. In an independent dust removing tower or the like instead of a desulfurization tower, the absorption liquid tank 6 is naturally a water tank for industrial water or the like.

【0016】次に前記構成の排煙脱硫装置により本発明
の除塵方法を用いて、ディ−ゼル発電設備から排出され
る排ガス中のダストを除去する作用について述べる。脱
硫塔1に接続した吸収液供給管dの噴霧ノズルから、充
填床2上に吸収液を均一散布する。この吸収液の供給
は、液溜り槽4から循環ポンプP1により脱硫吸収液を
抜き出し、吸収液循環流路cを経て供給されるが、必要
により吸収液タンク6から吸収液供給ポンプP2を介し
て吸収液供給流路eを経て供給される新たな脱硫吸収液
と混合され、吸収液供給管dを経て送給される。
Next, an operation of removing dust in exhaust gas discharged from diesel power generation equipment by using the dust removing method of the present invention using the flue gas desulfurization apparatus having the above-described structure will be described. From the spray nozzle of the absorption liquid supply pipe d connected to the desulfurization tower 1, the absorption liquid is uniformly sprayed on the packed bed 2. The absorption liquid is supplied from the liquid storage tank 4 by extracting the desulfurization absorption liquid by the circulation pump P1 and supplied through the absorption liquid circulation flow path c. If necessary, the absorption liquid is supplied from the absorption liquid tank 6 through the absorption liquid supply pump P2. It is mixed with a new desulfurization absorption liquid supplied through the absorption liquid supply passage e, and is supplied through the absorption liquid supply pipe d.

【0017】未燃焼カ−ボンや未燃焼油分などのダスト
及び硫黄酸化物などを含有するディ−ゼル発電設備から
排出された被処理ガスは、被処理ガスの導入口aから脱
硫塔1の充填床2の下方に導入され、充填床2を下降流
通する吸収液と向流接触しながら上昇し、向流接触する
間に、脱硫吸収液に硫黄酸化物が吸収されると共に、ダ
ストが捕集され脱硫吸収液中に分散される。硫黄酸化物
やダストが除去された被処理ガスは、上昇してエリミネ
−タ3で主にミストが分離され、清浄化された処理ガス
として塔頂部の排出煙道5を経て大気中に放出される。
Gas to be treated discharged from diesel power generation equipment containing dust and sulfur oxides such as unburned carbon and unburned oil is charged into the desulfurization tower 1 through an inlet a for the gas to be treated. It is introduced below the bed 2 and rises in countercurrent contact with the absorbent flowing down the packed bed 2 while flowing countercurrently. During the countercurrent contact, sulfur oxides are absorbed by the desulfurization absorbent and dust is collected. And dispersed in the desulfurization absorption liquid. The gas to be treated from which the sulfur oxides and dusts have been removed rises, the mist is mainly separated by the eliminator 3, and is discharged into the atmosphere via the exhaust flue 5 at the top of the tower as a purified treatment gas. You.

【0018】また、ダストを捕集した脱硫吸収液は下降
して塔底部の液溜り槽4に貯留され、一部は吸収液排出
管bから系外の排水処理装置に送られ、一部は循環ポン
プP1により抜き出され、吸収液として循環される。
The desulfurized absorbing liquid that has collected the dust descends and is stored in the liquid storage tank 4 at the bottom of the tower, and a part is sent from the absorbing liquid discharge pipe b to a wastewater treatment device outside the system, and a part is discharged. It is withdrawn by the circulation pump P1 and circulated as an absorbent.

【0019】前記脱硫吸収液には、界面活性剤タンク7
から界面活性剤供給ポンプP3及び消泡剤タンク8から
消泡剤供給ポンプP4により夫々の供給管g、fを経て
界面活性剤及び消泡剤が添加される。また、脱硫吸収液
としては、水酸化マグネシウム水溶液が用いられ、界面
活性剤としてはノニオン系界面活性剤を用いるのが好ま
しいが、本発明の除塵方法では、それらの吸収液や界面
活性剤には限定されない。
The desulfurization absorption liquid contains a surfactant tank 7
The surfactant and the defoamer are added via the respective supply pipes g and f by the surfactant supply pump P3 and the defoamer supply pump P4 from the defoamer tank 8. As the desulfurization absorbing solution, an aqueous solution of magnesium hydroxide is used, and as the surfactant, it is preferable to use a nonionic surfactant. However, in the dust removal method of the present invention, the absorbing solution and the surfactant are used. Not limited.

【0020】前記において、脱硫吸収液に界面活性剤が
添加されていることにより、水溶液に対して濡れ性が低
い未燃焼カ−ボンや未燃焼油分などのダストでも、濡れ
性が改善されて捕集分散されやすくなるため、捕集効率
が高くなる。また、吸収液に消泡剤が添加されているこ
とにより、ダストの濡れ性が改善されると共に、界面活
性剤により発泡しやすくなった脱硫吸収液の発泡を抑制
することができる。
In the above, by adding a surfactant to the desulfurization absorbing solution, even wet dust having low wettability to an aqueous solution, such as unburned carbon or unburned oil, has improved wettability and is trapped. Since the particles are easily collected and dispersed, the collection efficiency is increased. In addition, by adding an antifoaming agent to the absorbing liquid, the wettability of dust is improved, and foaming of the desulfurizing absorbing liquid, which is easily foamed by the surfactant, can be suppressed.

【0021】なお、界面活性剤の添加量は、50〜20
0ppmが好ましく、更に好ましくは70〜100pp
mであり、50ppm未満ではダストの捕集分散効果が
少なく、200ppmより多いとパ−ジ液中のCODが
高くなり、排水処理装置の負担が大きくなる。また、消
泡剤の添加量は、1〜20ppmが好ましく、更に好ま
しくは4〜10ppmであり、1ppm未満では消泡効
果が少なく、10ppmより多いと、消泡効果の大幅な
向上は見込めず、その割には薬品費用が嵩む問題があ
る。
The amount of the surfactant added is 50 to 20.
0 ppm is preferable, and 70-100 pp is more preferable.
If it is less than 50 ppm, the effect of collecting and dispersing dust is small, and if it is more than 200 ppm, the COD in the purge liquid increases, and the burden on the wastewater treatment apparatus increases. Further, the addition amount of the defoaming agent is preferably from 1 to 20 ppm, more preferably from 4 to 10 ppm. If it is less than 1 ppm, the defoaming effect is small, and if it is more than 10 ppm, a significant improvement in the defoaming effect cannot be expected, However, there is a problem that the cost of chemicals increases.

【0022】吸収液排出管bから抜き出された脱硫吸収
液は、図示しない排水処理装置により処理され、河川な
どに放流されるが、脱硫吸収液中に分散されたダスト
は、排水処理装置に付設される濾過機などで容易に分離
処理することができる。
The desulfurized absorbing solution extracted from the absorbing solution discharge pipe b is treated by a wastewater treatment device (not shown) and discharged to a river or the like. Dust dispersed in the desulfurized absorbing solution is discharged to the wastewater treatment device. Separation processing can be easily performed using an attached filter or the like.

【0023】(実施例)界面活性剤及び消泡剤の効果を
確認するため、脱硫吸収液として水酸化マグネシウム水
溶液(Mg(OH)2:2wt%溶液)を500ml使
用し、ディ−ゼル排ガスから採取したダスト13mgを
混合し、温度60℃で15秒攪拌してダストの分散効果
を観察した。 1.界面活性剤及び消泡剤添加ぜず:分散せず。 2.ノニオン系界面活性剤70ppm添加:分散効果有
るが、著しく発泡する。 3.ノニオン系界面活性剤50ppm添加:分散効果有
るが、著しく発泡する。 4.ノニオン系界面活性剤70ppm+消泡剤4ppm
添加:分散効果、発泡抑制効果有り。 5.ノニオン系界面活性剤70ppm+消泡剤10pp
m添加:分散効果、発泡抑制効果有るが、COD160
ppmで、COD増加量は界面活性剤添加量の約1.6
倍であった。
(Example) In order to confirm the effects of a surfactant and an antifoaming agent, 500 ml of a magnesium hydroxide aqueous solution (Mg (OH) 2: 2 wt% solution) was used as a desulfurization absorption solution, and diesel exhaust gas was used. 13 mg of the collected dust was mixed and stirred at a temperature of 60 ° C. for 15 seconds to observe a dust dispersion effect. 1. No surfactant and no defoamer added: no dispersion. 2. Nonionic surfactant added at 70 ppm: has a dispersing effect but remarkably foams. 3. Addition of 50 ppm of nonionic surfactant: It has a dispersing effect, but remarkably foams. 4. Nonionic surfactant 70ppm + defoamer 4ppm
Addition: Dispersion effect, foam suppression effect. 5. Nonionic surfactant 70ppm + antifoamer 10pp
m addition: COD160, although there is a dispersing effect and a foam suppressing effect
In ppm, the COD increase is about 1.6 times the amount of surfactant added.
It was twice.

【0024】[0024]

【発明の効果】本発明は、廉価な設備費でダストを含有
する排ガス中のダストを効率よく捕集することができ、
特に、ディ−ゼル機関から排出される排ガス中の未燃焼
カ−ボンや未燃焼油分などの、水溶液に対して濡れ性が
低いダストでも高い捕集効率で除去することができると
共に、捕集後の処理も容易な湿式除塵方法である。
According to the present invention, dust in exhaust gas containing dust can be efficiently collected at low equipment cost.
In particular, dust having low wettability with respect to an aqueous solution, such as unburned carbon and unburned oil in exhaust gas discharged from a diesel engine, can be removed with high collection efficiency. Is also an easy wet dust removal method.

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

【図1】本発明の一実施の形態の排ガスの湿式除塵方法
を適用した排煙脱硫装置の系統図
FIG. 1 is a system diagram of a flue gas desulfurization apparatus to which a wet dust removal method for exhaust gas according to an embodiment of the present invention is applied.

【符号の説明】[Explanation of symbols]

1:脱硫塔 2:充填床 3:エリミネ−タ 4:液溜り槽 5:処理ガスの排出煙道 6:吸収液タンク 7:界面活性剤タンク 8:消泡剤タンク 1: Desulfurization tower 2: Packed bed 3: Eliminator 4: Liquid storage tank 5: Flue gas for discharging treated gas 6: Absorbent tank 7: Surfactant tank 8: Defoamer tank

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 3G091 AA06 AA18 AB15 BA13 CA15 4D002 AA02 AC01 AC10 BA02 BA14 BA16 CA01 CA02 CA04 CA07 DA06 DA12 DA64 DA70 EA02 4D032 AB03 BB05 BB07 DA01  ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 3G091 AA06 AA18 AB15 BA13 CA15 4D002 AA02 AC01 AC10 BA02 BA14 BA16 CA01 CA02 CA04 CA07 DA06 DA12 DA64 DA70 EA02 4D032 AB03 BB05 BB07 DA01

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】ダストを含有する排ガス中のダストを水溶
液と接触させて捕集する湿式除塵方法において、水溶液
に界面活性剤を添加したことを特徴とする排ガスの湿式
除塵方法。
1. A wet dust removal method for collecting dust by contacting dust in an exhaust gas containing dust with an aqueous solution, wherein a surfactant is added to the aqueous solution.
【請求項2】ダストを含有する排ガス中のダストを水溶
液と接触させて捕集する湿式除塵方法において、水溶液
に界面活性剤及び消泡剤を添加したことを特徴とする排
ガスの湿式除塵方法。
2. A wet dust removal method for collecting dust by contacting dust in exhaust gas containing dust with an aqueous solution, wherein a surfactant and an antifoaming agent are added to the aqueous solution.
【請求項3】ダストを含有する排ガスがディ−ゼル機関
から排出される排ガスであることを特徴とする請求項1
又は請求項2記載の排ガスの湿式除塵方法。
3. The exhaust gas containing dust is exhaust gas discharged from a diesel engine.
Or the wet dust removal method for exhaust gas according to claim 2.
【請求項4】水溶液が排ガス中の硫黄酸化物を除去する
脱硫吸収液であることを特徴とする請求項1〜請求項3
のいずれか1項記載の排ガスの湿式除塵方法。
4. The desulfurization absorbing solution for removing sulfur oxides in exhaust gas as an aqueous solution.
The wet dust removal method for exhaust gas according to any one of the above.
JP2000182477A 2000-06-19 2000-06-19 Wet dust collecting method for exhaust gas Pending JP2002001042A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000182477A JP2002001042A (en) 2000-06-19 2000-06-19 Wet dust collecting method for exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000182477A JP2002001042A (en) 2000-06-19 2000-06-19 Wet dust collecting method for exhaust gas

Publications (1)

Publication Number Publication Date
JP2002001042A true JP2002001042A (en) 2002-01-08

Family

ID=18683226

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000182477A Pending JP2002001042A (en) 2000-06-19 2000-06-19 Wet dust collecting method for exhaust gas

Country Status (1)

Country Link
JP (1) JP2002001042A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
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WO2010076853A1 (en) * 2008-12-30 2010-07-08 Uehara Kyomasa Method for dust removal and cleaning of polluted gas by water washing
EP2275190A3 (en) * 2009-07-17 2011-03-02 Mitsubishi Heavy Industries, Ltd. Spray scrubber with defoamer spray unit
WO2012153706A1 (en) * 2011-05-11 2012-11-15 川崎重工業株式会社 Wet exhaust gas purification device
WO2012153705A1 (en) * 2011-05-11 2012-11-15 川崎重工業株式会社 Wet exhaust gas purification device
KR20150092950A (en) * 2014-02-06 2015-08-17 정동길 Wet and Dry Type High Efficiency Dust Collector
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* Cited by examiner, † Cited by third party
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JP5514742B2 (en) * 2008-12-30 2014-06-04 京正 上原 Flushing dust removal and purification equipment for polluted gases
JPWO2010076853A1 (en) * 2008-12-30 2012-06-21 上原 京正 Washing-type dust removal purification method for polluted gases
WO2010076853A1 (en) * 2008-12-30 2010-07-08 Uehara Kyomasa Method for dust removal and cleaning of polluted gas by water washing
EP2275190A3 (en) * 2009-07-17 2011-03-02 Mitsubishi Heavy Industries, Ltd. Spray scrubber with defoamer spray unit
EP2361666A1 (en) * 2009-07-17 2011-08-31 Mitsubishi Heavy Industries, Ltd. Spray scrubber with defoamer spray unit
US8741033B2 (en) 2009-07-17 2014-06-03 Mitsubishi Heavy Industries, Ltd. Air pollution control apparatus
WO2012153706A1 (en) * 2011-05-11 2012-11-15 川崎重工業株式会社 Wet exhaust gas purification device
JP2012236143A (en) * 2011-05-11 2012-12-06 Kawasaki Heavy Ind Ltd Wet exhaust gas purification device
WO2012153705A1 (en) * 2011-05-11 2012-11-15 川崎重工業株式会社 Wet exhaust gas purification device
KR20140048131A (en) * 2011-05-11 2014-04-23 가와사키 쥬코교 가부시키가이샤 Wet exhaust gas purification device
KR101655736B1 (en) * 2011-05-11 2016-09-08 가와사키 쥬코교 가부시키가이샤 (디/비/에이 가와사키 헤비 인더스트리즈, 리미티드) Wet exhaust gas purification device
KR20150092950A (en) * 2014-02-06 2015-08-17 정동길 Wet and Dry Type High Efficiency Dust Collector
KR101589804B1 (en) * 2014-02-06 2016-02-01 정동길 Wet and Dry Type High Efficiency Dust Collector
CN112516713A (en) * 2020-12-15 2021-03-19 广东电网有限责任公司电力科学研究院 Spray dust-settling agent and preparation method and application thereof

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