JPH11347362A - Catalytic board for flue gas desulfurization - Google Patents
Catalytic board for flue gas desulfurizationInfo
- Publication number
- JPH11347362A JPH11347362A JP10160378A JP16037898A JPH11347362A JP H11347362 A JPH11347362 A JP H11347362A JP 10160378 A JP10160378 A JP 10160378A JP 16037898 A JP16037898 A JP 16037898A JP H11347362 A JPH11347362 A JP H11347362A
- Authority
- JP
- Japan
- Prior art keywords
- carbon fiber
- core board
- activated carbon
- board
- active carbon
- 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
- 238000006477 desulfuration reaction Methods 0.000 title claims abstract description 52
- 230000023556 desulfurization Effects 0.000 title claims abstract description 52
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims description 14
- 239000003546 flue gas Substances 0.000 title claims description 14
- 230000003197 catalytic effect Effects 0.000 title 1
- 238000006243 chemical reaction Methods 0.000 claims abstract description 35
- 239000003054 catalyst Substances 0.000 claims abstract description 21
- 229920000049 Carbon (fiber) Polymers 0.000 claims abstract description 15
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 20
- 230000000149 penetrating effect Effects 0.000 claims description 4
- 239000011247 coating layer Substances 0.000 claims description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 abstract description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 27
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 abstract description 22
- 239000004917 carbon fiber Substances 0.000 abstract description 8
- 239000003365 glass fiber Substances 0.000 abstract description 4
- 239000000463 material Substances 0.000 abstract description 2
- 238000004080 punching Methods 0.000 abstract description 2
- 230000035515 penetration Effects 0.000 abstract 1
- 239000011162 core material Substances 0.000 description 19
- 239000007789 gas Substances 0.000 description 17
- 239000010410 layer Substances 0.000 description 15
- 238000010521 absorption reaction Methods 0.000 description 10
- 238000000034 method Methods 0.000 description 9
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 5
- 238000001816 cooling Methods 0.000 description 4
- 229910052815 sulfur oxide Inorganic materials 0.000 description 4
- 239000002250 absorbent Substances 0.000 description 3
- 230000002745 absorbent Effects 0.000 description 3
- 239000010440 gypsum Substances 0.000 description 3
- 229910052602 gypsum Inorganic materials 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 229920002239 polyacrylonitrile Polymers 0.000 description 3
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical group [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 229920002678 cellulose Polymers 0.000 description 2
- 239000001913 cellulose Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 239000012299 nitrogen atmosphere Substances 0.000 description 2
- 230000000717 retained effect Effects 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 229910052717 sulfur Inorganic materials 0.000 description 2
- 239000011593 sulfur Substances 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 239000012298 atmosphere Substances 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 230000002209 hydrophobic effect Effects 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
- -1 polypropylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、各種燃料を燃焼さ
せるボイラ、ガスタービン、エンジン、燃焼炉等から排
出される排ガス中の硫黄酸化物(SOX )を除去する際
に用いる排煙脱硫用触媒ボードに関する。The present invention relates to the boiler for burning various fuels, for flue gas desulfurization to be used for removing a gas turbine, engine, sulfur oxides in exhaust gas discharged from a combustion furnace or the like (SO X) It relates to a catalyst board.
【0002】[0002]
【従来の技術】従来、排ガス中の硫黄酸化物の除去方法
として、石灰石または消石灰スラリーを吸収剤として用
いて、硫黄分を石膏として回収する石灰−石膏法が採用
されている。他の方法として、活性炭による吸着法が知
られている。2. Description of the Related Art Hitherto, as a method for removing sulfur oxides from exhaust gas, a lime-gypsum method of recovering sulfur content as gypsum using limestone or slaked lime slurry as an absorbent has been adopted. As another method, an adsorption method using activated carbon is known.
【0003】[0003]
【発明が解決しようとする課題】従来の石灰−石膏法で
は、多量の水および硫黄酸化物の吸収剤が必要である。
そのため、脱硫設備の大型化や複雑化が避けられない。
また、活性炭による吸着法の場合、活性炭に吸着した硫
黄分を水洗によって脱離させるため、大量の水を必要と
する。しかも、この方法の場合、生成した希硫酸の廃棄
や、吸着材の乾燥処理等が必要になる。本発明者らは、
硫黄酸化物の吸収剤や大型の脱硫設備を必要としない簡
易な排煙脱硫方法を検討した結果、脱硫反応用活性炭素
繊維を触媒として、排ガス中のSO2 をSO3 に酸化
し、更にSO3 と水との反応によって硫酸を得る方法を
見い出している。本発明は、この方法をより効率的に実
施するための排煙脱硫用触媒ボードを提供するものであ
る。The conventional lime-gypsum process requires large amounts of water and sulfur oxide absorbents.
For this reason, the size and complexity of the desulfurization equipment cannot be avoided.
In addition, in the case of the adsorption method using activated carbon, a large amount of water is required because sulfur adsorbed on activated carbon is desorbed by washing with water. In addition, in the case of this method, it is necessary to discard the generated dilute sulfuric acid and to dry the adsorbent. We have:
Results of studying a simple flue gas desulfurization process that does not require an absorbent and large desulfurization of sulfur oxides, the desulfurization reaction activated carbon fiber as a catalyst to oxidize the SO 2 in the flue gas to SO 3, further SO They have found a way to obtain sulfuric acid by reacting 3 with water. The present invention provides a flue gas desulfurization catalyst board for performing this method more efficiently.
【0004】[0004]
【課題を解決するための手段】本発明の排煙脱硫用触媒
ボードは、両面に亘って貫通する多数の孔を有する芯材
ボードと、該芯材ボードの孔の内部を充填し、かつ、該
芯材ボードの両面に被覆層を形成する脱硫反応用活性炭
素繊維とからなることを特徴とする(請求項1)。According to the present invention, there is provided a flue gas desulfurization catalyst board comprising a core board having a large number of holes penetrating on both sides, filling the inside of the hole of the core board, and The core board is made of activated carbon fibers for a desulfurization reaction forming a coating layer on both sides (claim 1).
【0005】[0005]
【発明の実施の形態】本発明で用いる芯材ボードは、グ
ラスファイバー、ポリプロピレンファイバー等の材質か
らなる。芯材ボードの厚みは、通常、0.1〜1.0m
m程度である。芯材ボードは、その両面に亘って貫通す
る多数の孔を有する。孔は、その内部に充填される脱硫
反応用活性炭素繊維と、芯材ボードの両面上に形成され
る脱硫反応用活性炭素繊維層を連絡するためのものであ
り、任意の断面形状を採り得る。両面に亘って貫通する
多数の孔を有する芯材ボードの例としては、グラスファ
イバーボードをパンチングしたものや、グラスファイバ
ー製のメッシュボード等が挙げられる。DESCRIPTION OF THE PREFERRED EMBODIMENTS A core board used in the present invention is made of a material such as glass fiber or polypropylene fiber. The thickness of the core board is usually 0.1 to 1.0 m
m. The core board has a number of holes penetrating on both sides thereof. The hole is for connecting the activated carbon fiber for desulfurization reaction filled therein and the activated carbon fiber layer for desulfurization reaction formed on both surfaces of the core material board, and can take any cross-sectional shape. . Examples of a core board having a large number of holes penetrating both sides include a punched glass fiber board, a mesh board made of glass fiber, and the like.
【0006】芯材ボードとして、パンチングしたボード
を用いる場合、孔の直径は、例えば、0.2〜5mm程
度であり、孔同士の間隔は、中心間の距離で、例えば、
0.5〜10mm程度である。芯材ボードとして、メッ
シュボードを用いる場合、芯材のワイヤーの直径は、例
えば、0.05〜0.2mm程度であり、メッシュ同士
の間隔(格子間隔)は、例えば、0.1〜2mm程度で
ある。パンチングしたボードを芯材ボードとして用いた
場合の脱硫用触媒ボードの断面図を図1に示す。図1に
おいて、芯材ボード1の多数の孔2の内部には、脱硫反
応用活性炭素繊維3が充填されると共に、芯材ボード1
の両面には、脱硫反応用活性炭素繊維層4,5が形成さ
れている。When a punched board is used as the core board, the diameter of the holes is, for example, about 0.2 to 5 mm, and the distance between the holes is the distance between the centers.
It is about 0.5 to 10 mm. When a mesh board is used as the core board, the diameter of the core wire is, for example, about 0.05 to 0.2 mm, and the spacing between the meshes (grid spacing) is, for example, about 0.1 to 2 mm. It is. FIG. 1 is a cross-sectional view of a desulfurization catalyst board when a punched board is used as a core board. In FIG. 1, the inside of a large number of holes 2 of a core board 1 is filled with activated carbon fibers 3 for desulfurization,
Activated carbon fiber layers 4 and 5 for desulfurization reaction are formed on both surfaces of.
【0007】本発明の排煙脱硫用触媒ボード(以下、単
に「触媒ボード」ともいう。)は、芯材ボードの両面に
形成された脱硫反応用活性炭素繊維層が、芯材ボードの
孔の内部の脱硫反応用活性炭素繊維によって連絡された
構造となっているので、水分が、触媒ボード内に良好に
浸透する。すなわち、孔のない芯材ボードの両面に脱硫
反応用活性炭素繊維層を形成させた場合と比べて、触媒
ボードの表面からの任意の深さにおける水分の保持量が
大きくなり、脱硫反応が促進される。また、脱硫反応用
活性炭素繊維層の芯材ボードへの密着性が高まる。[0007] The flue gas desulfurization catalyst board of the present invention (hereinafter simply referred to as "catalyst board") has a structure in which activated carbon fiber layers for desulfurization reaction formed on both sides of the core board have holes in the core board. Since the structure is connected by the activated carbon fiber for the desulfurization reaction, the moisture permeates well into the catalyst board. That is, as compared with the case where the activated carbon fiber layers for desulfurization reaction are formed on both sides of the core board having no holes, the amount of retained water at an arbitrary depth from the surface of the catalyst board is increased, and the desulfurization reaction is accelerated. Is done. In addition, the adhesion of the activated carbon fiber layer for the desulfurization reaction to the core board increases.
【0008】本発明で用いる脱硫反応用活性炭素繊維
は、排ガス中のSO2 がSO3 に酸化する際に触媒とし
て働く。本発明で用いる脱硫反応用活性炭素繊維の製造
方法を以下、説明する。原料となる活性炭素繊維の種類
としては、特に制限はなく、ピッチ系、ポリアクリロニ
トリル系、フェノール系、セルロース系等の活性炭素繊
維を用いることができる。これらの中でも、特に活性炭
素繊維の表面の疎水性のより高いものが望ましく、具体
的にはピッチ系活性炭素繊維等を挙げることができる。The activated carbon fiber for desulfurization reaction used in the present invention functions as a catalyst when SO 2 in exhaust gas is oxidized to SO 3 . The method for producing the activated carbon fiber for desulfurization reaction used in the present invention will be described below. The type of activated carbon fiber used as a raw material is not particularly limited, and active carbon fibers such as pitch-based, polyacrylonitrile-based, phenol-based, and cellulose-based activated carbon fibers can be used. Among these, those having higher hydrophobicity on the surface of the activated carbon fiber are particularly desirable, and specific examples thereof include pitch-based activated carbon fiber.
【0009】活性炭素繊維は、窒素ガス等の非酸化雰囲
気下で、通常600〜1,200℃程度の温度で熱処理
される。処理時間は、処理温度等に応じて適宜定めれば
よい。この熱処理により、本発明で用いる脱硫反応用炭
素繊維を得ることができる。脱硫反応用活性炭素繊維
は、熱処理により親水性である酸素官能基の一部または
全部がCO、CO2 等として除去されているので、処理
前に比べて疎水性の大きな表面となっている。このた
め、SO2 の酸化活性点へのSO2 の吸着が容易に起こ
り、しかも生成する硫酸の排出も速やかに進行する結
果、触媒の機能が阻害されることなく、脱硫反応が促進
される。Activated carbon fibers are usually heat-treated at a temperature of about 600 to 1200 ° C. in a non-oxidizing atmosphere such as nitrogen gas. The processing time may be appropriately determined according to the processing temperature and the like. By this heat treatment, the carbon fiber for desulfurization reaction used in the present invention can be obtained. The activated carbon fiber for the desulfurization reaction has a surface that is more hydrophobic than that before the treatment, since part or all of the hydrophilic oxygen functional groups are removed as CO, CO 2, or the like by heat treatment. Therefore, it occurs readily snapping SO 2 to oxidized active sites SO 2, yet produced results that discharge also proceeds rapidly sulfate, without the function of the catalyst is inhibited, the desulfurization reaction is accelerated.
【0010】脱硫反応用活性炭素繊維の製造例の具体例
は、例えば、次の通りである。具体例1 ピッチ系活性炭素繊維(「OG−20A」、アドール
(株)製)を用い、これを窒素雰囲気中で900〜1,
200℃の温度範囲内で1時間焼成する。具体例2 ポリアクリロニトリル系活性炭素繊維(「FE−30
0」、東邦レーヨン(株)製)を用い、これを窒素雰囲
気中で800〜1,200℃の温度範囲内で1時間焼成
する。A specific example of a production example of an activated carbon fiber for a desulfurization reaction is as follows, for example. Specific Example 1 A pitch-based activated carbon fiber (“OG-20A”, manufactured by Adol Co., Ltd.) was used in a nitrogen atmosphere at 900 to 1,
Baking is performed for 1 hour in a temperature range of 200 ° C. Specific Example 2 Polyacrylonitrile-based activated carbon fiber (“FE-30
0 "(manufactured by Toho Rayon Co., Ltd.) and fired in a nitrogen atmosphere within a temperature range of 800 to 1200 ° C. for 1 hour.
【0011】本発明で用いられる脱硫反応用活性炭素繊
維の性状は、通常、太さが7〜20μm、比表面積が5
00〜2,500m2 /g、外表面積が0.2〜2.0
m2/g、細孔直径が45オングストローム以下であ
る。ピッチ系、ポリアクリロニトリル系、フェノール
系、セルロース系の各脱硫反応用活性炭素繊維の組成式
等を表1に示す。なお、表1中の数値は、通常の値を示
すにすぎず、これらの数値範囲外のものも存在し得る。The activated carbon fibers for desulfurization reaction used in the present invention generally have a thickness of 7 to 20 μm and a specific surface area of 5 μm.
00 to 2,500 m 2 / g, outer surface area 0.2 to 2.0
m 2 / g, and the pore diameter is 45 Å or less. Table 1 shows the composition formulas and the like of the activated carbon fibers for each of the pitch-based, polyacrylonitrile-based, phenol-based, and cellulose-based desulfurization reactions. Note that the numerical values in Table 1 indicate only normal values, and there may be values outside these numerical ranges.
【0012】[0012]
【表1】 [Table 1]
【0013】本発明の排煙脱硫用触媒ボードの製造方法
は、以下の通りである。メッシュボードあるいはパンチ
ングボードを芯材とし、両面へ活性炭素繊維層(ボー
ド)を合わせて、加熱(80〜110℃)、加圧(3〜
10kg/cm2 G)下で融着させる。The method for producing the flue gas desulfurization catalyst board of the present invention is as follows. A mesh board or a punching board is used as a core material, and activated carbon fiber layers (boards) are combined on both sides, and heated (80 to 110 ° C) and pressurized (3 to
Fusing under 10 kg / cm 2 G).
【0014】本発明の排煙脱硫用触媒ボードを用いた排
煙脱硫システムの一例を、図1を参照しつつ説明する。
図1において、ボイラ11から排出された硫黄酸化物を
含有する排ガスは、ガス−ガスヒータ(GGH)13に
よって冷却された後、集塵器(ESP)14内で除塵さ
れ、ファン12を経由して、導入口15から吸収塔16
内に導入される。吸収塔16への導入時の排ガスの温度
は、90℃程度である。吸収塔内に導入された排ガス
は、排ガスの増湿冷却用の水の散布器17から散布され
る水と接触して、70℃以下に冷却されると共に、相対
湿度が増加し、通常、飽和状態(相対湿度=100%)
となる。ここで、温度が70℃を超えると、脱硫用活性
炭素繊維層での水分の蒸発量が多くなり、水の供給量を
大きくしなければならないという不都合がある。An example of a flue gas desulfurization system using the flue gas desulfurization catalyst board of the present invention will be described with reference to FIG.
In FIG. 1, an exhaust gas containing sulfur oxides discharged from a boiler 11 is cooled by a gas-gas heater (GGH) 13, then is dust-removed in a dust collector (ESP) 14, and passes through a fan 12. From the inlet 15 to the absorption tower 16
Introduced within. The temperature of the exhaust gas at the time of introduction into the absorption tower 16 is about 90 ° C. The exhaust gas introduced into the absorption tower comes in contact with water sprayed from a water sprayer 17 for humidifying and cooling the exhaust gas, and is cooled to 70 ° C. or lower, and the relative humidity increases. Condition (relative humidity = 100%)
Becomes Here, if the temperature exceeds 70 ° C., the amount of evaporation of water in the activated carbon fiber layer for desulfurization increases, and there is a disadvantage that the supply amount of water must be increased.
【0015】増湿冷却された排ガスは、吸収塔16内の
中央部に充填されている脱硫反応用活性炭素繊維層18
内を下方に向かって通過する。なお、脱硫反応用活性炭
素繊維層18は、予め、脱硫反応用活性炭素繊維層18
の上方または近傍に設けられる水の供給器19によって
水を供給し、活性炭素繊維の表面に水が付着した状態と
しておく。ここで、脱硫反応用活性炭素繊維層18は、
例えば、ボックス状のフレーム内に本発明の触媒ボード
を一定間隔で縦に多数並べたものを、吸収塔内に設置す
ることによって形成することができる。The exhaust gas which has been subjected to the humidified cooling is supplied to the activated carbon fiber layer 18 for desulfurization reaction filled in the central portion of the absorption tower 16.
Passing down inside. In addition, the activated carbon fiber layer 18 for desulfurization reaction is
Is supplied by a water supply device 19 provided above or in the vicinity of the activated carbon fiber so that water adheres to the surface of the activated carbon fiber. Here, the activated carbon fiber layer for desulfurization reaction 18
For example, the catalyst board of the present invention can be formed by arranging a large number of the catalyst boards of the present invention in a box-shaped frame at regular intervals in an absorption tower.
【0016】排ガス中のSO2 は、触媒として作用する
脱硫反応用活性炭素繊維の表面で、排ガス中の酸素(O
2 )と反応し、SO3 に酸化される。生成したSO
3 は、脱硫反応用活性炭素繊維に付着している水と反応
して、硫酸(H2 SO4 )となる。生成した硫酸は、脱
硫反応用活性炭素繊維層18から落下して、吸収塔16
の底部から排出され、ポンプ20を経て、硫酸貯留槽2
1に貯留され、工業用に用いられる。SO 2 in the exhaust gas is converted into oxygen (O 2 ) in the exhaust gas on the surface of the activated carbon fiber for the desulfurization reaction acting as a catalyst.
2 ) and is oxidized to SO 3 . Generated SO
3 reacts with water adhering to the activated carbon fiber for desulfurization reaction to form sulfuric acid (H 2 SO 4 ). The generated sulfuric acid falls from the activated carbon fiber layer for desulfurization reaction 18 and is absorbed by the absorption tower 16.
Is discharged from the bottom of the tank and passed through the pump 20 to be in the sulfuric acid storage tank 2.
Stored in 1 and used for industry.
【0017】排ガスの増湿冷却用の水として、系外から
導入される水を用いるか、または、図示するように、吸
収塔の下部から排出される水(希硫酸)をポンプ22に
よって循環させて用いることができる。循環水を用いる
と、水の使用量を節減することができる。脱硫反応用活
性炭素繊維層18に硫酸生成用に供給される水について
も、同様に、系外からの水または吸収塔から排出される
循環水を用いることができる。排ガスの増湿冷却用の水
の散布器17と、脱硫反応用活性炭素繊維層への硫酸生
成用の水の供給器19は、兼用してもよい。吸収塔16
内で脱硫された排ガスは、吸収塔16の下部の排出口2
3から排出されて、ガス−ガスヒータ13で加熱された
後、煙突24から排出される。As the water for humidifying and cooling the exhaust gas, water introduced from outside the system is used, or water (dilute sulfuric acid) discharged from the lower part of the absorption tower is circulated by a pump 22 as shown in the figure. Can be used. The use of circulating water can reduce the amount of water used. Similarly, as the water supplied to the activated carbon fiber layer 18 for desulfurization reaction for producing sulfuric acid, water from outside the system or circulating water discharged from the absorption tower can be used. The water sprayer 17 for humidifying and cooling the exhaust gas and the water supplier 19 for generating sulfuric acid to the activated carbon fiber layer for the desulfurization reaction may be shared. Absorption tower 16
Exhaust gas desulfurized in the exhaust port 2
3, and after being heated by the gas-gas heater 13, is discharged from the chimney 24.
【0018】[0018]
【発明の効果】本発明の排煙脱硫用触媒ボードによれ
ば、ボード内の水分保持量が大きくなり、脱硫反応が促
進される。According to the flue gas desulfurization catalyst board of the present invention, the amount of water retained in the board is increased, and the desulfurization reaction is accelerated.
【図1】本発明の排煙脱硫用触媒ボードの断面図であ
る。FIG. 1 is a cross-sectional view of a flue gas desulfurization catalyst board of the present invention.
【図2】本発明の脱硫用触媒ボードを用いた排煙脱硫シ
ステムの一例を示す概略図である。FIG. 2 is a schematic view showing an example of a flue gas desulfurization system using the desulfurization catalyst board of the present invention.
1 芯材ボード 2 孔 3 脱硫反応用活性炭素繊維 4,5 脱硫反応用活性炭素繊維層 11 ボイラ 12 ファン 13 ガス−ガスヒータ 14 集塵器 15 導入口 16 吸収塔 17 水の散布器 18 脱硫反応用活性炭素繊維層 19 水の供給器 20 ポンプ 21 硫酸貯留槽 22 ポンプ 23 排出口 24 煙突 REFERENCE SIGNS LIST 1 core board 2 hole 3 activated carbon fiber for desulfurization reaction 4,5 activated carbon fiber layer for desulfurization reaction 11 boiler 12 fan 13 gas-gas heater 14 dust collector 15 inlet 16 absorption tower 17 water sprayer 18 for desulfurization reaction Activated carbon fiber layer 19 Water supplier 20 Pump 21 Sulfuric acid storage tank 22 Pump 23 Outlet 24 Chimney
Claims (1)
芯材ボードと、該芯材ボードの孔の内部を充填し、か
つ、該芯材ボードの両面に被覆層を形成する脱硫反応用
活性炭素繊維とからなることを特徴とする排煙脱硫用触
媒ボード。A core board having a large number of holes penetrating both sides thereof, and a desulfurization reaction for filling the inside of the holes of the core board and forming coating layers on both sides of the core board A flue gas desulfurization catalyst board comprising activated carbon fibers.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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JP16037898A JP3600441B2 (en) | 1998-06-09 | 1998-06-09 | Catalyst board for flue gas desulfurization |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16037898A JP3600441B2 (en) | 1998-06-09 | 1998-06-09 | Catalyst board for flue gas desulfurization |
Publications (2)
Publication Number | Publication Date |
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JPH11347362A true JPH11347362A (en) | 1999-12-21 |
JP3600441B2 JP3600441B2 (en) | 2004-12-15 |
Family
ID=15713680
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JP16037898A Expired - Fee Related JP3600441B2 (en) | 1998-06-09 | 1998-06-09 | Catalyst board for flue gas desulfurization |
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JP (1) | JP3600441B2 (en) |
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1998
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