JPH11319477A - Treatment of combustion waste gas from fossil fuel - Google Patents

Treatment of combustion waste gas from fossil fuel

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Publication number
JPH11319477A
JPH11319477A JP10130152A JP13015298A JPH11319477A JP H11319477 A JPH11319477 A JP H11319477A JP 10130152 A JP10130152 A JP 10130152A JP 13015298 A JP13015298 A JP 13015298A JP H11319477 A JPH11319477 A JP H11319477A
Authority
JP
Japan
Prior art keywords
sodium carbonate
flue
waste gas
mol
fossil fuel
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
JP10130152A
Other languages
Japanese (ja)
Inventor
Takehiko Morimoto
武彦 森本
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP10130152A priority Critical patent/JPH11319477A/en
Publication of JPH11319477A publication Critical patent/JPH11319477A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To efficiently and safely neutralize and remove sulfur oxides (SOx) in combustion waste gas of fossil fuel by adding an aq. soln. of sodium carbonate (including natural soda) to the combustion waste gas of fossil fuel in the flue in the downstream of the combustion device. SOLUTION: As for the position where an aq. soln. of sodium carbonate is added to the combustion waste gas of fossil fuel, the flue in the downstream of the combustion device, namely, a proper position is selected according to the purpose among the positions before the air preheater 4, between the air preheater 4 and electric dust collector 5, between the electric dust collector 5 and desulfurizing device 6, and between the desulfurizing device 6 and a funnel 7. In this method, 0.1 to 20 wt.% sodium carbonate aq. soln. is added by 0.01 to 20 mol to 1 mol of SO3 in the waste gas, preferably 0.01 to 10 mol. Thereby, sulfur oxides (SOx) produced when a fuel containing sulfur is used in a boiler or the like can be efficiently and safely neutralized, and therefore, problems mainly caused by sulfur oxides can be prevented.

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、化石燃料の燃焼排
ガスの中和処理方法に関し、さらに詳しくはボイラ等で
硫黄分を含有する燃料の使用により発生する硫黄酸化物
(SOX)を効率良くかつ安全に中和処理して除去し、
硫黄酸化物が主たる原因となる障害を抑制する方法に関
する。
BACKGROUND OF THE INVENTION The present invention relates to a neutralizing treatment method of the combustion exhaust gas of fossil fuel, and more particularly sulfur oxides generated by the use of fuels containing sulfur in a boiler or the like (SO X) and efficiently And safely neutralized and removed,
The present invention relates to a method for suppressing a failure mainly caused by a sulfur oxide.

【0002】[0002]

【従来の技術】硫黄分を含む燃料を使用すると必ずSO
3 が排ガス中に含有し、腐食性等に大きく影響するの
で、従釆SO3 の問題は燃料中にカルシウム、マグネシ
ウムの酸化物とか水酸化物等を油スラリーにして燃料中
に添加注入して低温域で中和させていた。この方法はボ
イラの熱交換部に添加物が多量に堆積して運転等に支障
を来す関係から、その多量の使用が困難であった。
2. Description of the Related Art When a fuel containing sulfur is used, SO
Since 3 is contained in exhaust gas and greatly affects corrosiveness, the problem of conventional SO 3 is to add calcium and magnesium oxides or hydroxides to the fuel as an oil slurry and add it to the fuel. Neutralized in the low temperature range. In this method, it is difficult to use a large amount of the additive because a large amount of the additive is deposited on the heat exchange section of the boiler and hinders operation and the like.

【0003】又、煙道途中での中和を積極的にする方法
として、水酸化カルシウム、酸化マグネシウム、水酸化
マグネシウム等の粉体とか、水スラリーを空気予熱器
(AH:エァーヒーター)後の煙道に添加注入してい
た。この方法で粉体の場合は、粉塵が貯蔵注入装置付近
に散乱し、作業環境を著しく悪くする。加えて注入方法
でスクリューフィダー等を使用する関係から、定量性が
悪く安定的な効果が得にくい場合がある。水スラリーを
煙道に使用する例では、注入移送ラインに堆積して詰ま
り、安定的に使用するのに大きな問題があつた。
[0003] As a method of positively neutralizing in the middle of the flue, powder such as calcium hydroxide, magnesium oxide, magnesium hydroxide or the like, or a water slurry after an air preheater (AH: air heater) is used. The additive was injected into the flue. In the case of powder in this manner, dust is scattered near the storage and injection device, significantly deteriorating the working environment. In addition, due to the use of a screw feeder or the like in the injection method, there are cases where the quantitative effect is poor and a stable effect cannot be obtained. In the case of using a water slurry for a flue, there is a serious problem in that the slurry is deposited and clogged in an injection transfer line and is stably used.

【0004】さらに、アンモニアを煙道にガス化して注
入させているが、効果の面で酸性硫酸アンモニウムが生
成されて新たな酸性降下煤塵の発生原因となる。
Further, ammonia is gasified and injected into the flue. However, in terms of effect, ammonium ammonium sulfate is generated, which causes a new generation of acid dust.

【0005】電気集塵器では腐食防止と集塵効率の向上
を得るためにアンモニアの注入が広く実施されている
が、荷電不良の原因になっており、防止策としてMgO
の粉体等の添加がなされている。しかし、アンモニア
の注入は取り扱い上規制が多く、危険度も高く、大きな
課題になっている。
[0005] In an electric precipitator, ammonia is widely injected to prevent corrosion and improve dust collection efficiency. However, it causes charging failure, and MgO is used as a preventive measure.
Powder and the like have been added. However, injection of ammonia has many restrictions on handling, has a high degree of danger, and is a major problem.

【0006】湿式の排煙脱硫装置、例えば、水酸化ナト
リウム水溶液等を煙道に噴霧する装置では、SO2とS
3との反応速度の相違により、排煙中のSO2は除去す
ることができるが、SO3は除去できない。そして、S
2ではなく、SO3が白煙の原因になる。即ち、湿式の
排煙脱硫装置では、SO3が急冷されて硫酸ミストが生
成し、硫酸ミストが白煙として観察される。
In a wet-type flue gas desulfurization apparatus, for example, an apparatus for spraying an aqueous solution of sodium hydroxide into a flue, SO 2 and S 2 are used.
Due to the difference in the reaction rate with O 3 , SO 2 in the flue gas can be removed, but SO 3 cannot be removed. And S
SO 3 instead of O 2 causes white smoke. That is, in a wet type flue gas desulfurization apparatus, SO 3 is rapidly cooled to generate sulfuric acid mist, and the sulfuric acid mist is observed as white smoke.

【0007】白煙対策として、MgO 粉体を排煙脱硫
装置の前に添加し、SO3 と硫酸ミストとを中和するこ
とにより、白煙のたなびきを減少させることができる。
しかし、粉体の投入は定量性が低く、白煙の減少効果は
不安定であり、あまり利用されていない。
[0007] As a countermeasure against white smoke, MgO powder is added before the flue gas desulfurization device to neutralize SO 3 and sulfuric acid mist, whereby fluttering of white smoke can be reduced.
However, the introduction of the powder has a low quantitative property, and the effect of reducing white smoke is unstable, so that it is not used much.

【0008】[0008]

【発明が解決しようとする課題】化石燃料の燃焼排ガ
ス、例えばボイラ等で硫黄分を含有する燃料の使用によ
り発生する硫黄酸化物(SOX)を、効率良くかつ安全
に中和処理して除去する方法の改善が切望されている。
SUMMARY OF THE INVENTION Emissions of fossil fuel combustion exhaust gas, for example, sulfur oxides (SO x ) generated by the use of a fuel containing sulfur in a boiler or the like, are efficiently and safely neutralized and removed. There is a coveted improvement in the way you do it.

【0009】本発明は、化石燃料の燃焼排ガス中の硫黄
酸化物(SOX)を、効率良くかつ安全に中和処理して
除去する方法を提供することを目的とする。この方法に
よりボイラ等の稼働率の低下の抑制と安定な運転得るこ
とにある。
It is an object of the present invention to provide a method for efficiently and safely neutralizing and removing sulfur oxides (SO x ) in fossil fuel combustion exhaust gas. It is an object of the present invention to suppress a decrease in the operating rate of a boiler or the like and to obtain a stable operation.

【0010】本発明の他の目的は、硫黄酸化物(S
X)が、空気予熱器、電気集塵器、煙道側壁等におい
て、排ガスが冷却された箇所で露点に達するとH2SO4
になり、これにより発生する腐食とか閉塞障害を抑制す
ることである。
Another object of the present invention is to provide a sulfur oxide (S
O X) is an air preheater, electrostatic precipitator, in the flue side wall or the like, H 2 SO 4 reaches the dew point at the point where the exhaust gas is cooled
It is to suppress the corrosion and the obstruction failure generated thereby.

【0011】煙道等で堆積した煤塵は、負荷変動等によ
りpHの低い硫酸を多く含有した塊として排出して、酸
性降下煤塵になり環境悪化をまねく。従って、本発明
は、この煤塵の発生を抑制することも目的とする。
Dust deposited in a flue or the like is discharged as a lump containing a large amount of sulfuric acid having a low pH due to load fluctuation or the like, resulting in acidic fallen dust, leading to environmental degradation. Therefore, an object of the present invention is to suppress the generation of the dust.

【0012】さらに、本発明は、ボイラ等の稼働率及び
効率の低下を抑制するとともに、長期間にわたり安定な
運転を可能とすることも目的とする。
Still another object of the present invention is to suppress a decrease in the operation rate and efficiency of a boiler or the like and to enable stable operation for a long period of time.

【0013】[0013]

【課題を解決するための手段】本発明の化石燃料の燃焼
排ガスの処理方法は、化石燃料の燃焼排ガスに炭酸ナト
リウム(天然ソーダを含む)水溶液を、該燃焼装置の下
流の煙道に添加し、中和処理する排ガスの処理方法であ
る。
According to the present invention, there is provided a method for treating fossil fuel combustion exhaust gas, comprising adding a sodium carbonate (including natural soda) aqueous solution to a fossil fuel combustion exhaust gas to a flue downstream of the combustion apparatus. And a method for treating exhaust gas to be neutralized.

【0014】本発明では、0.1〜20重量%の炭酸ナ
トリウム水溶液を、排ガス中のSO3の1モルに対して
0.01〜20モル添加することが好ましく、0.01
〜10モル添加することが更に好ましく、0.01〜6
モル添加することが更になお好ましい。
In the present invention, it is preferable to add 0.1 to 20% by weight of an aqueous solution of sodium carbonate in an amount of 0.01 to 20 mol per mol of SO 3 in the exhaust gas.
More preferably, it is added in an amount of 0.01 to 6 mol.
It is even more preferred to add them in molar.

【0015】本明細書において、煙道とは、ボイラ等の
燃焼装置の排ガスの流路を意味し、煙突内部の流路をも
含む。
In this specification, the flue means a flow path of exhaust gas from a combustion device such as a boiler, and also includes a flow path inside a chimney.

【0016】本発明において、化石燃料の燃焼排ガスに
炭酸ナトリウム水溶液を注入する箇所は、図1に示すよ
うに、燃焼装置の下流の煙道、すなわち、空気予熱器4
の前、空気予熱器4と電気集塵器5との間、電気集塵器
5と脱硫装置6との間、脱硫装置6と煙突7の間の煙
道、並びに、煙突7の内部の煙道があるが、その目的に
応じて適宜選択される。
In the present invention, as shown in FIG. 1, the point where the aqueous solution of sodium carbonate is injected into the flue gas of fossil fuel is located in the flue downstream of the combustion device, that is, the air preheater 4.
Before, between the air preheater 4 and the electric precipitator 5, between the electric precipitator 5 and the desulfurizer 6, the flue between the desulfurizer 6 and the chimney 7, and the smoke inside the chimney 7. Although there is a way, it is appropriately selected according to the purpose.

【0017】化石燃料には、石油、重油、石炭等が含ま
れる。特に、硫黄の含有量が比較的に高い重油、石炭の
場合に、本発明を好適に適用することができる。
[0017] Fossil fuels include petroleum, heavy oil, coal and the like. In particular, the present invention can be suitably applied to heavy oil and coal having a relatively high sulfur content.

【0018】炭酸ナトリウム水溶液の濃度が、0.1%
未満では使用量が多くなりすぎて、タンクや移送ポンプ
大きくなり、実用の限界と同時に添加位置の煙道底部に
蒸発しきれない水滴が溜まる形跡があり、錆の発生して
いる煙道部が観察されている。他方、20%を超えると
冬季での低温下で安定に溶解できず、又結晶が析出する
おそれがある。
The concentration of the aqueous sodium carbonate solution is 0.1%
If it is less than the amount used, the tank or transfer pump becomes too large, and at the same time as the limit of practical use, there is evidence that water vapor that cannot be completely evaporated collects at the bottom of the flue at the addition position, and the flue where rust is generated Has been observed. On the other hand, if it exceeds 20%, it cannot be stably dissolved at a low temperature in winter, and crystals may be precipitated.

【0019】空気予熱器のSO3による閉塞と腐食の予
防には、炭酸ナトリウム水溶液を、SO3の1モルに対
して0.01〜当モルを燃焼装置と空気予熱器との間の
煙道に噴射することが好ましい。
To prevent clogging and corrosion of the air preheater by SO 3, an aqueous solution of sodium carbonate is used in an amount of 0.01 to equimolar with respect to 1 mol of SO 3 to the flue between the combustion device and the air preheater. It is preferable to spray.

【0020】酸性降下煤塵の抑制には、炭酸ナトリウム
水溶液を、煤塵量に対して1〜20重量%を空気予熱器
と電気集塵器との間の煙道に噴射することが好ましい。
In order to suppress the acid deposition dust, it is preferable to inject the aqueous solution of sodium carbonate into the flue between the air preheater and the electrostatic precipitator in an amount of 1 to 20% by weight based on the amount of the dust.

【0021】電気集塵器の荷電不良抑制とアンモニア削
減には、炭酸ナトリウム水溶液を、煤塵量に対して1〜
20重量%を空気予熱器と電気集塵器との間の煙道に噴
射することが好ましい。
In order to suppress the charging failure of the electrostatic precipitator and to reduce the ammonia, the aqueous solution of sodium carbonate is used in an amount of 1-
Preferably, 20% by weight is injected into the flue between the air preheater and the electrostatic precipitator.

【0022】電気集塵器にアンモニアの注入を炭酸ナト
リウム水溶液に置き換える場合での範囲は、炭酸ナトリ
ウム水溶液を、SO3の1モルに対して1〜20モルを
空気予熱器と電気集塵器の間の煙道に噴射することが好
ましく、1〜10モルを空気予熱器と電気集塵器の間の
煙道に噴射することが更に好ましい。
In the case where the injection of ammonia into the electrostatic precipitator is replaced with an aqueous sodium carbonate solution, the range of the aqueous sodium carbonate solution is from 1 to 20 mol per mol of SO 3 to the air preheater and the electric precipitator. Preferably, it is injected into the flue in between, more preferably from 1 to 10 mol is injected into the flue between the air preheater and the electrostatic precipitator.

【0023】排煙脱硫装置等の白煙のたなびき抑制に
は、炭酸ナトリウム水溶液を硫酸ミスト(SO3の1モ
ルに換算)に対して0.1〜20モルを電気集塵器と脱
硫装置との間の煙道に噴射することが好ましく、0.1
〜10モルを電気集塵器と脱硫装置との間の煙道に噴射
することが更に好ましい。
In order to suppress fluttering of white smoke in a flue gas desulfurization apparatus or the like, 0.1 to 20 mol of an aqueous sodium carbonate solution with respect to a sulfuric acid mist (converted to 1 mol of SO 3 ) is used by an electric dust collector and a desulfurization apparatus. It is preferable to inject into the flue between
More preferably, 10 to 10 moles are injected into the flue between the electrostatic precipitator and the desulfurizer.

【0024】炭酸ナトリウム水溶液の相対的な添加量
は、煙道中の煙の流速に依存する。一般的には、流速が
速い場合には、炭酸ナトリウム水溶液の添加量が増加す
る傾向にある。また、炭酸ナトリウム水溶液の添加量を
多くすることにより、排ガスの温度を低下させることが
可能となり、ボイラ効率が向上する。
The relative addition amount of the aqueous sodium carbonate solution depends on the flow rate of the smoke in the flue. Generally, when the flow rate is high, the amount of the added sodium carbonate aqueous solution tends to increase. Also, by increasing the amount of the aqueous sodium carbonate solution, the temperature of the exhaust gas can be lowered, and the boiler efficiency is improved.

【0025】以下に、炭酸ナトリウム水溶液の使用の特
徴を説明する。 1. 炭酸ナトリウム水溶液を高温の排ガス中に噴露し
て微細に注入すると、粉体等の固体に比較して微細な粒
子が得られる。さらに、水滴が蒸発する前、水滴表面が
温度低く、硫黄酸化物特にSO3 は吸着溶解し易いので
大変に迅速な中和が行なえる。 2. 中和剤として炭酸ナトリウムの使用は、アンモニ
アに比較して高圧ガス取り扱いと劇毒物等の規制がなく
安全に取り扱える。 3. 水溶液であるので、粉体に比較して正確に注入で
き安定かつ正確な中和が出来る。 4. スラリーと違い沈殿などなく、移送ラインとか噴
射ノズルの詰まりも殆どなく、装置の管理が容易であり
安定な運転が可能になる。 5. 排ガスの温度を低下させたときであっても、煙道
が詰まらないので、ボイラ効率が向上する。
The characteristics of the use of the aqueous sodium carbonate solution will be described below. 1. When an aqueous sodium carbonate solution is spouted into a high-temperature exhaust gas and injected finely, fine particles are obtained as compared with a solid such as a powder. Further, before the water droplet evaporates, the temperature of the water droplet surface is low, and sulfur oxides, especially SO 3, are easily adsorbed and dissolved, so that very quick neutralization can be performed. 2. The use of sodium carbonate as a neutralizing agent allows safe handling because there is no regulation of high-pressure gas and noxious poisons as compared with ammonia. 3. Since it is an aqueous solution, it can be injected more accurately than powder, and stable and accurate neutralization can be performed. 4. Unlike slurry, there is no sedimentation, there is almost no clogging of transfer lines and injection nozzles, and the management of the apparatus is easy and stable operation is possible. 5. Even when the temperature of the exhaust gas is lowered, the flue is not clogged, so that the boiler efficiency is improved.

【0026】[0026]

【実施例】実施例1 炭酸ナトリウム水溶液を圧縮空気にてダイヤフラム式比
例注入ポンプで4kg/cm2の圧力下、ボイラと空気
予熱器4との間の煙道に噴射した。この場合において、
空気予熱器のSO3 による詰まりで必要とする水洗回数
とテストピースによる腐食量の試験を実施した。使用し
たテストピースは普通鋼であり、元の重量は12.5g
であった。テスト時のボイラ仕様とテスト時の排ガス組
成は、次の通りである。
EXAMPLE 1 An aqueous solution of sodium carbonate was injected into a flue between a boiler and an air preheater 4 with compressed air at a pressure of 4 kg / cm 2 by a diaphragm type proportional injection pump. In this case,
A test was performed on the number of times of water washing required for clogging of the air preheater with SO 3 and the amount of corrosion by a test piece. The test piece used is plain steel and the original weight is 12.5g
Met. The boiler specifications during the test and the exhaust gas composition during the test are as follows.

【0027】テスト時のボイラ仕様 型式 自然循環式 蒸発量 2 8 6T/H 蒸気温度 540℃ 蒸気圧力 120Kg/cm2 テスト時の排ガス組成 CO2 11% O2 1.5% SO2 1150ppm SO3 65ppmBoiler specifications during test Model Natural circulation type Evaporation amount 28 8 T / H Steam temperature 540 ° C Steam pressure 120 kg / cm 2 Exhaust gas composition at test CO 2 11% O 2 1.5% SO 2 1150 ppm SO 3 65 ppm

【0028】図1に示すボイラ及び煙道を用いた。ボイ
ラは、火炉1と火炉1を加熱するための加熱器と、エコ
ー部2を有する。そして、ボイラの排ガス出口と、煙突
7との間には、煙道が形成されている。煙道には、空気
予熱器4、排ガス中の煤塵を除去するための電気集塵器
5、及び、ナトリウム水溶液を噴霧する湿式の脱硫装置
6がこの順序で上流から下流に配置されている。
The boiler and the flue shown in FIG. 1 were used. The boiler has a furnace 1, a heater for heating the furnace 1, and an echo unit 2. A flue is formed between the exhaust gas outlet of the boiler and the chimney 7. In the stack, an air preheater 4, an electric precipitator 5 for removing dust in exhaust gas, and a wet desulfurization device 6 for spraying a sodium aqueous solution are arranged in this order from upstream to downstream.

【0029】炭酸ナトリウム水溶液の水滴で高温ガスに
噴霧されるので、水の蒸発潜熱の関係からSO3 はH2
SO4として結露し、さらにSO3 が水滴表面に濃縮さ
れ事から効率よく反応して、無害なNa2SO4になる。
試験結果を表1に示す。
Since the high-temperature gas is sprayed with water droplets of the aqueous solution of sodium carbonate, SO 3 is converted to H 2 from the relation of latent heat of evaporation of water.
Condensation occurs as SO 4 , and furthermore, SO 3 is concentrated on the surface of the water droplets, so that it reacts efficiently and becomes harmless Na 2 SO 4 .
Table 1 shows the test results.

【0030】[0030]

【表1】 [Table 1]

【0031】SO3 に対して当モルの炭酸ナトリウム水
溶液を添加すると、一年間運転中に詰まりがなくて一度
の水洗も必要なく、かつテストピースによる腐食量で9
3%近く減少し、稼働率の向上と空気予熱器の寿命の延
長が期待できる。なお、僅か0.01モルの炭酸ナトリ
ウム水溶液の添加により、添加以前では3ケ月に1回程
度の水洗を行っていたものが、年間を通じて水洗回数が
1回程度ですむように改善され、かつ腐食で7 0%近
く減少している。
When an aqueous solution of sodium carbonate equivalent to the amount of SO 3 is added, there is no clogging during one year of operation, there is no need to wash once, and the corrosion amount by the test piece is 9%.
It is expected to decrease by nearly 3%, improve the operation rate and extend the life of the air preheater. By adding only 0.01 mol of sodium carbonate aqueous solution, water washing was performed about once every three months before the addition, but the number of times of water washing was improved to about once throughout the year, and corrosion was reduced by 7 times. It has decreased by almost 0%.

【0032】炭酸ナトリウム水溶液を煙道に添加する場
合には、空気予熱器の出口ガス温度を160℃から12
5℃に低下させたときであっても、詰まりによる差圧上
昇が観察されなかった。このように出口ガス温度を低下
させることにより、ボイラ効率が91%から92.5%
に向上し、省エネルギーとなった。ボイラのような完成
度が高い技術分野では、ボイラそのものの改良による熱
効率の向上はほぼ限界になっており、このように1.5
%の上昇は顕著な効果である。また、炭酸ナトリウム水
溶液の添加量が多い場合には、更に排ガス温度の低下が
可能になり、更に省エネルギーとなりうる。
When the aqueous sodium carbonate solution is added to the flue, the outlet gas temperature of the air preheater is increased from 160 ° C to 12 ° C.
Even when the temperature was lowered to 5 ° C., no increase in differential pressure due to clogging was observed. By lowering the outlet gas temperature in this way, the boiler efficiency can be increased from 91% to 92.5%.
To save energy. In a technical field with a high degree of perfection such as a boiler, the improvement of the thermal efficiency by improving the boiler itself is almost at its limit.
A rise in% is a noticeable effect. In addition, when the amount of the aqueous sodium carbonate solution is large, the temperature of the exhaust gas can be further reduced, which can further save energy.

【0033】炭酸ナトリウム水溶液の濃度は、0.1〜
20重量%の範囲で使用して変化みたが基本的には差が
なく、炭酸ナトリウム水溶液のSO3 に対するモル比の
方が大きい影響を有する。
The concentration of the aqueous sodium carbonate solution is from 0.1 to
Although the amount was changed in the range of 20% by weight, there was basically no difference, and the molar ratio of the aqueous solution of sodium carbonate to SO 3 had a greater effect.

【0034】実施例2 炭酸ナトリウム水溶液を実施例1におけると同様に空気
予熱器と電気集塵器との間の煙道に噴射した場合におけ
る、電気集塵器灰のpHと酸性降下煤塵に対する影響を
調べる試験を実施した。テスト時のボイラ仕様と排ガス
組成は、実施例1と同じである。試験結果を表2に示
す。
Example 2 Influence on pH and Acid Deposition Dust of Electrostatic Precipitator Ash when an aqueous sodium carbonate solution was injected into the flue between the air preheater and the electrostatic precipitator as in Example 1. A test was conducted to determine The boiler specifications and the exhaust gas composition during the test are the same as in Example 1. Table 2 shows the test results.

【0035】[0035]

【表2】 [Table 2]

【0036】炭酸ナトリウム水溶液の添加は、電気集塵
器灰のpHと酸性降下煤塵に対し大きな影響をもち、十
分効果の達成が認められる。
The addition of the aqueous solution of sodium carbonate has a great effect on the pH of the ash and the fall of acid dust, and it is recognized that a sufficient effect is achieved.

【0037】従来、酸性降下煤塵のpHを4 以上にす
るには、燃料中に多量のマグネシウム、カルシウム等の
添加が必要であったが、あまり多く添加すると添加剤成
分が火炉等に堆積して熱交換などが悪くなり、排ガス温
度が著しく上昇する例が多く、ボイラの長期安定運転に
支障を来す場合もあった。この為にMgO 、CaOの
粉体又はスラリーを添加する方法が採られていたが、粉
体の場合は定量性が悪く、安定した効果が得られない欠
点があった。又、粉体の場合、注入装置の廻りが汚れ、
作業環境が劣悪になっている。スラリーの場合は貯蔵タ
ンク底部の堆積と注入ラインの詰まり等が発生して、管
理に人手が多くかかり安定した注入が困難であった。こ
の点、本発明は水溶液を使用するので全く障害なく、安
定に運転が可能になり、十分効果が得られる。
Conventionally, it was necessary to add a large amount of magnesium, calcium, etc. to the fuel in order to raise the pH of the acid dust to 4 or more. However, if too much is added, the additive components accumulate in a furnace or the like. In many cases, the heat exchange and the like have deteriorated, and the exhaust gas temperature has increased remarkably, which has sometimes hindered long-term stable operation of the boiler. For this reason, a method of adding MgO 2 or CaO powder or slurry has been adopted. However, in the case of powder, there is a drawback that the quantitative effect is poor and a stable effect cannot be obtained. In the case of powder, the area around the injection device becomes dirty,
The working environment is poor. In the case of slurry, accumulation at the bottom of the storage tank, clogging of the injection line, and the like occurred, and it required a lot of manpower for management, and stable injection was difficult. In this regard, since the present invention uses an aqueous solution, stable operation can be performed without any hindrance, and a sufficient effect can be obtained.

【0038】この実施例2では、更に炭酸ナトリウム水
溶液の添加により、電気集塵器の荷電不良の防止に顕著
な効果が確認された。従来、電気集塵器ではSO3とH2
SO4による腐食防止として、アンモニアを電気集塵器
入口前の煙道に注入しているが、一部酸性硫安が生成し
て放電極に付着する。このために電圧値が高くなり、ハ
ンチング現象が現れて荷電不良の障害が起きる。荷電不
良は、大気汚染の原因の煤塵規制値を一時的にオーバー
する様になる関係から、運転を停止して水洗をすること
もある。炭酸ナトリウムはアルカリ性物質であるから煤
塵の電気固有抵抗値を上昇させ、同時に電気集塵器灰の
pHをも上昇させて酸性硫安を正硫安化させる様にな
る。この結果として電気集塵器灰の吸湿性が少なくな
り、流動性が改善されて電気集塵器の詰まりが改善され
ることになる。pHが上昇した事から、アンモニアの注
入量を50%以上の削減が出来る。そして排ガス中のS
3 の1モルに対して、炭酸ナトリウム水溶液の濃度を
炭酸ナトリウム濃度0.1〜20重量%の範囲で変化さ
せて、炭酸ナトリウム分として1〜20モルの範囲で、
空気予熱器と電気集塵器との間の煙道中に添加するとp
Hは7近くなり、アンモニア注入を停止してもpH5〜
6の範囲で推移する事から、アンモニアの代価品になる
事が証明された。この現象は、ナトリウム塩は硫酸ナト
リウムを形成するが、酸性硫酸ナトリウムがpH4 以
上では殆ど生成されないことによる。アンモニア注入に
は、液体アンモニアの貯蔵と気化装置等が必要であり、
法規的には高圧ガス、劇毒物、労働安全、可燃ガス規制
がある。アンモニアに比較して炭酸ナトリウムは安価で
あり、そのうえ設備的にも規制もなく、安全性が高く、
簡単な装置ですみ、取り扱いと貯蔵がアンモニアに比較
して簡易である。従って、経済的な改善は大きな値にな
る。炭酸ナトリワム水溶液添加と電気集塵器(灰)の荷
電状況の試験結果を表3に示す。
In Example 2, it was confirmed that the addition of the aqueous solution of sodium carbonate had a remarkable effect in preventing charging failure of the electrostatic precipitator. Conventionally, SO 3 and H 2
To prevent corrosion by SO 4 , ammonia is injected into the flue in front of the entrance of the electrostatic precipitator, but some acidic ammonium sulfate is generated and adheres to the discharge electrode. For this reason, the voltage value increases, a hunting phenomenon appears, and a failure of charging failure occurs. Since the charging failure temporarily exceeds the dust regulation value that causes air pollution, the operation may be stopped and the water may be washed. Since sodium carbonate is an alkaline substance, it raises the electrical resistivity of the dust and at the same time raises the pH of the ash of the electrostatic precipitator, thereby converting acidic ammonium sulfate to normal ammonium sulfate. As a result, the hygroscopicity of the electric precipitator ash is reduced, the flowability is improved, and the clogging of the electric precipitator is improved. Since the pH has risen, the injection amount of ammonia can be reduced by 50% or more. And S in the exhaust gas
With respect to 1 mol of O 3 , the concentration of the aqueous sodium carbonate solution was changed in the range of 0.1 to 20% by weight of sodium carbonate, and in the range of 1 to 20 mol as sodium carbonate,
When added into the flue between the air preheater and the electrostatic precipitator, p
H becomes close to 7 and pH 5
It was proved that it could be used as a substitute for ammonia, because it remained in the range of 6. This phenomenon is due to the fact that sodium salts form sodium sulphate, but little sodium sulphate is produced above pH4. Ammonia injection requires storage and vaporization of liquid ammonia, etc.
There are laws and regulations on high-pressure gas, toxic substances, occupational safety, and flammable gas. Sodium carbonate is cheaper than ammonia, and there are no restrictions on equipment and safety,
With simple equipment, it is easier to handle and store than ammonia. Therefore, the economic improvement is of great value. Table 3 shows the test results of the addition of the aqueous solution of sodium carbonate and the charging status of the electrostatic precipitator (ash).

【0039】[0039]

【表3】 [Table 3]

【0040】また、湿式脱硫装置から排出される白煙が
長くたなびく現象があり、一種の公害的な状況になって
いる。上記表3の試験の時に白煙が短くなる事が観察さ
れた。白煙の主原因は、SO3 が脱硫装置内の脱硫水と
接触する過程で急冷されて硫酸ミストができる為であ
る。本発明の炭酸ナトリウム水溶液は、水滴表面にSO
3 を結露吸収と濃縮により、SO3 を硫酸ナリウムにし
て白煙の水分気化を促進する。炭酸ナトリウム水溶液を
電気集塵器と脱硫装置との間の煙道に、実施例1に記載
と同様に噴射した場合における、添加と白煙の関係につ
き、表4に示す。表4中の炭酸ナトリウム水溶液の量
は、SO3の1モルに対するモル量である。
Further, there is a phenomenon in which white smoke discharged from the wet desulfurization apparatus flutters for a long time, which is a kind of pollution. During the tests in Table 3 above, it was observed that white smoke was shortened. The main cause of the white smoke is that SO 3 is rapidly cooled in the process of contacting with the desulfurization water in the desulfurization device, thereby producing sulfuric acid mist. The aqueous solution of sodium carbonate of the present invention has an
3 is desorbed by condensation and concentrated to convert SO 3 into sodium sulfate to promote the vaporization of white smoke. Table 4 shows the relationship between addition and white smoke when the aqueous sodium carbonate solution was injected into the flue between the electrostatic precipitator and the desulfurizer in the same manner as described in Example 1. The amount of the aqueous sodium carbonate solution in Table 4 is a molar amount based on 1 mol of SO 3 .

【0041】[0041]

【表4】 [Table 4]

【0042】炭酸ナトリウム水溶液添加と白煙の関係
は、白煙のたなびきを目視で観察した値であるが、僅か
に炭酸ナトリウム水溶液が添加されますと明確に短くな
っている事が認められる。
The relationship between the addition of the aqueous sodium carbonate solution and the white smoke is a value obtained by visually observing the fluttering of the white smoke, and it is recognized that the addition of the aqueous sodium carbonate solution slightly shortens the relationship.

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

【図1】化石燃料の燃焼排ガスの処理方法の工程概略図
である。
FIG. 1 is a process schematic diagram of a method for treating a combustion exhaust gas of a fossil fuel.

【符号の説明】[Explanation of symbols]

1…火炉、2…エコー部、3…加熱器、4…空気予熱
器、5…電気集塵器、6…脱硫装置、7…煙突
DESCRIPTION OF SYMBOLS 1 ... Furnace, 2 ... Echo part, 3 ... Heater, 4 ... Air preheater, 5 ... Electric precipitator, 6 ... Desulfurizer, 7 ... Chimney

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 化石燃料の燃焼排ガスに炭酸ナトリウム
水溶液を、該燃焼装置の下流の煙道に添加し、中和処理
することを特徴とする排ガスの処理方法。
1. A method for treating exhaust gas, comprising adding an aqueous solution of sodium carbonate to a flue gas of fossil fuel to a flue downstream of the combustion device and neutralizing the flue gas.
【請求項2】 0.1〜20重量%の炭酸ナトリウム水
溶液を、排ガス中のSO3の1モルに対して0.01〜
20モル添加する請求項1に記載の方法。
2. An aqueous solution of 0.1 to 20% by weight of sodium carbonate is used in an amount of 0.01 to 1 mol of SO 3 in exhaust gas.
The method according to claim 1, wherein 20 mol is added.
JP10130152A 1998-05-13 1998-05-13 Treatment of combustion waste gas from fossil fuel Pending JPH11319477A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10130152A JPH11319477A (en) 1998-05-13 1998-05-13 Treatment of combustion waste gas from fossil fuel

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10130152A JPH11319477A (en) 1998-05-13 1998-05-13 Treatment of combustion waste gas from fossil fuel

Publications (1)

Publication Number Publication Date
JPH11319477A true JPH11319477A (en) 1999-11-24

Family

ID=15027237

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10130152A Pending JPH11319477A (en) 1998-05-13 1998-05-13 Treatment of combustion waste gas from fossil fuel

Country Status (1)

Country Link
JP (1) JPH11319477A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001321636A (en) * 2000-05-17 2001-11-20 Asahi Glass Co Ltd Gas treating method
JP2001340727A (en) * 2000-05-31 2001-12-11 Asahi Glass Co Ltd Method for treating gas
JP2003001054A (en) * 2001-06-21 2003-01-07 Mitsubishi Heavy Ind Ltd Apparatus for removing so3 component in exhaust gas
JP2006326575A (en) * 2005-04-26 2006-12-07 Mitsubishi Heavy Ind Ltd Device and method of treating exhaust gas

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001321636A (en) * 2000-05-17 2001-11-20 Asahi Glass Co Ltd Gas treating method
JP2001340727A (en) * 2000-05-31 2001-12-11 Asahi Glass Co Ltd Method for treating gas
JP2003001054A (en) * 2001-06-21 2003-01-07 Mitsubishi Heavy Ind Ltd Apparatus for removing so3 component in exhaust gas
EP1402937A1 (en) * 2001-06-21 2004-03-31 Mitsubishi Heavy Industries, Ltd. So3 separating and removing equipment for flue gas
EP1402937A4 (en) * 2001-06-21 2007-08-08 Mitsubishi Heavy Ind Ltd So3 separating and removing equipment for flue gas
JP2006326575A (en) * 2005-04-26 2006-12-07 Mitsubishi Heavy Ind Ltd Device and method of treating exhaust gas

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