JPH04358518A - Desulfurizing agent blowing device - Google Patents
Desulfurizing agent blowing deviceInfo
- Publication number
- JPH04358518A JPH04358518A JP3030373A JP3037391A JPH04358518A JP H04358518 A JPH04358518 A JP H04358518A JP 3030373 A JP3030373 A JP 3030373A JP 3037391 A JP3037391 A JP 3037391A JP H04358518 A JPH04358518 A JP H04358518A
- Authority
- JP
- Japan
- Prior art keywords
- nozzle
- desulfurizing agent
- desulfurization
- exhaust gas
- agent injection
- 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
Links
- 230000003009 desulfurizing effect Effects 0.000 title claims abstract description 88
- 238000007664 blowing Methods 0.000 title claims abstract description 9
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 98
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 36
- 230000023556 desulfurization Effects 0.000 claims abstract description 36
- 238000002347 injection Methods 0.000 claims description 36
- 239000007924 injection Substances 0.000 claims description 36
- 238000000034 method Methods 0.000 claims description 18
- 230000002378 acidificating effect Effects 0.000 claims description 5
- 238000002485 combustion reaction Methods 0.000 claims description 5
- 239000000126 substance Substances 0.000 claims description 4
- 238000000746 purification Methods 0.000 claims description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 28
- 238000006243 chemical reaction Methods 0.000 abstract description 10
- 238000009833 condensation Methods 0.000 abstract description 7
- 230000005494 condensation Effects 0.000 abstract description 7
- 230000002093 peripheral effect Effects 0.000 abstract description 5
- 230000000717 retained effect Effects 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 22
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 10
- 239000000920 calcium hydroxide Substances 0.000 description 10
- 235000011116 calcium hydroxide Nutrition 0.000 description 10
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 10
- 238000010586 diagram Methods 0.000 description 8
- 239000000428 dust Substances 0.000 description 6
- 239000000843 powder Substances 0.000 description 6
- 239000002002 slurry Substances 0.000 description 5
- 239000007921 spray Substances 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 239000000463 material Substances 0.000 description 3
- 238000007711 solidification Methods 0.000 description 3
- 230000008023 solidification Effects 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 239000012159 carrier gas Substances 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 239000000383 hazardous chemical Substances 0.000 description 2
- 150000003464 sulfur compounds Chemical class 0.000 description 2
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 230000001154 acute effect Effects 0.000 description 1
- 238000011276 addition treatment Methods 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 235000012255 calcium oxide Nutrition 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 231100000676 disease causative agent Toxicity 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 230000035515 penetration Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000003303 reheating Methods 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 238000011282 treatment Methods 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Nozzles (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明はボイラ等から排出される
排ガスの浄化装置に係り、特に脱硫剤吹込みノズルの結
露による脱硫剤の詰まりを防止するのに好適な脱硫剤吹
込み装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for purifying exhaust gas discharged from a boiler or the like, and more particularly to a desulfurizing agent injection apparatus suitable for preventing clogging of the desulfurizing agent due to dew condensation in the desulfurizing agent injection nozzle.
【0002】0002
【従来の技術】火力発電所における重油焚き、石炭焚き
ボイラから排出される排ガス中には、硫黄化合物(SO
x)やHClなどの酸性有害物質が通常、100〜30
00ppmの割合で含まれており、酸性雨や光化学スモ
ッグの原因物質となるため、その効果的な除去手段が強
く望まれている。従来から湿式法(例えば石灰石−石膏
法)又は乾式法(活性炭法)が実施されているが、湿式
法は有害物質の除去率が高い反面、廃水処理が困難であ
り、また排ガスを再加熱する必要があって、設備費およ
び運転費が高く、一方乾式法では高い除去率が得られな
いという問題があった。このため、排水処理の必要がな
く、運転費が低コストで高い除去率が得られる脱硫方法
の開発が望まれていた。[Prior Art] Sulfur compounds (SO
Acidic hazardous substances such as
It is contained at a ratio of 0.00 ppm and is a causative agent of acid rain and photochemical smog, so an effective means of removing it is strongly desired. Conventionally, wet methods (e.g. limestone-gypsum method) or dry methods (activated carbon method) have been used, but while the wet method has a high removal rate of harmful substances, it is difficult to treat wastewater and requires reheating of exhaust gas. However, the dry method has the problem of not being able to obtain a high removal rate. Therefore, it has been desired to develop a desulfurization method that does not require wastewater treatment, has low operating costs, and can provide a high removal rate.
【0003】ボイラなどの排ガスの脱硫法としては、上
記の方法のほかに、消石灰やそのスラリを排ガス中に噴
霧する半乾式法や火炉内や煙道内の高温ガス中に石灰石
を直接分散させて酸性有害物質を除去する乾式法などが
提案されており、これらは設備費や運転費が安いという
特徴を有しているが、いずれも脱硫率が低いという問題
があった。[0003] In addition to the above-mentioned methods, desulfurization methods for exhaust gas from boilers and the like include a semi-dry method in which slaked lime or its slurry is sprayed into the exhaust gas, and a method in which limestone is directly dispersed in the high-temperature gas in the furnace or flue. Dry methods for removing acidic harmful substances have been proposed, and although these methods have the advantage of low equipment and operating costs, they all have the problem of low desulfurization rates.
【0004】消石灰や生石灰を排ガス中に噴霧して排ガ
ス中のSOxと反応させ、これを集塵装置で除去する従
来法の代表的なフローシートを図5に示す。図において
、ボイラ1からの排ガス2は、エアヒータ3で熱交換さ
れ温度が低下し、脱硫塔4に導入される。消石灰などの
脱硫剤5は、煙道6または脱硫塔4内に噴霧し、この時
水も供給して排ガス2の温度を下げ、かつ湿度を上げる
。この際、水は脱硫剤5と別に供給しても、脱硫剤5を
スラリ7として同時に供給してもよい。反応した脱硫剤
5は、排ガス2中の灰とともに集塵装置8で捕集され、
廃棄されると同時に、煙突9からはクリーンなガスとし
て大気中に放出される。FIG. 5 shows a typical flow sheet of a conventional method in which slaked lime or quicklime is sprayed into exhaust gas to react with SOx in the exhaust gas, and then removed by a dust collector. In the figure, exhaust gas 2 from a boiler 1 undergoes heat exchange with an air heater 3 to lower its temperature, and is introduced into a desulfurization tower 4. A desulfurizing agent 5 such as slaked lime is sprayed into the flue 6 or the desulfurizing tower 4, and water is also supplied at this time to lower the temperature of the exhaust gas 2 and increase the humidity. At this time, water may be supplied separately from the desulfurizing agent 5, or the desulfurizing agent 5 may be supplied as a slurry 7 at the same time. The reacted desulfurizing agent 5 is collected together with the ash in the exhaust gas 2 by a dust collector 8,
At the same time as being disposed of, it is released into the atmosphere from the chimney 9 as clean gas.
【0005】このような方法で、排ガス処理を行う時、
脱硫剤5を供給する脱硫剤吹込みノズル11の内面に脱
硫剤5が固着し、目詰まりが生じて脱硫剤5のスムーズ
な導入が損なわれる。[0005] When performing exhaust gas treatment using such a method,
The desulfurizing agent 5 sticks to the inner surface of the desulfurizing agent injection nozzle 11 that supplies the desulfurizing agent 5, causing clogging and impairing the smooth introduction of the desulfurizing agent 5.
【0006】すなわち、図6に示したように、排煙脱硫
用の消石灰および水は、煙道6に設置した両ノズルから
吹き込むが、水噴霧ノズル12には脱硫剤吹込みノズル
11の上流側にあるのが一般的で、運転時には下流側の
脱硫剤吹込みノズル11の先端部が湿らされ、消石灰や
ダストが付着固化しやすい状態となって、ノズル孔が詰
まり消石灰のスムーズな吹込みを妨げるという問題があ
った。That is, as shown in FIG. 6, slaked lime and water for flue gas desulfurization are blown from both nozzles installed in the flue 6. During operation, the tip of the desulfurizing agent injection nozzle 11 on the downstream side becomes wet, making it easy for slaked lime and dust to adhere and harden, which clogs the nozzle hole and prevents smooth injection of slaked lime. There was a problem of interference.
【0007】[0007]
【発明が解決しようとする課題】上述したごとく、従来
の排煙脱硫装置において、脱硫剤を導入する導入管のノ
ズル部は、その上流側で水が導入されるために、煙道内
の排ガスが、約150℃から100℃前後にまで冷却さ
れ、同時に脱硫剤吹込みノズル部も冷却される。また、
脱硫剤吹込みノズル部はキャリアガスによっても冷却さ
れ、特に飽和温度(約54℃)以下にまで冷却されれば
、水蒸気が結露してノズル外周面に付着し、結露した水
分が脱硫剤吹込みノズル内面部にまで浸透する。[Problems to be Solved by the Invention] As mentioned above, in conventional flue gas desulfurization equipment, water is introduced at the upstream side of the nozzle section of the introduction pipe that introduces the desulfurization agent, so that the exhaust gas in the flue is , from about 150°C to around 100°C, and at the same time, the desulfurizing agent injection nozzle section is also cooled. Also,
The desulfurizing agent injection nozzle part is also cooled by the carrier gas, and in particular, if it is cooled to below the saturation temperature (approximately 54°C), water vapor will condense and adhere to the outer circumferential surface of the nozzle, and the condensed moisture will be used to inject the desulfurizing agent. Penetrates to the inner surface of the nozzle.
【0008】こうした状態で脱硫剤としての消石灰の粉
末を導入すると、脱硫剤吹込みノズル部に脱硫剤がたち
まち付着固化し、付着物がしだいに積層され堆積する。
すなわち、図7(a)〜(f)は脱硫剤吹込みノズル外
周面の結露が原因となる脱硫剤の付着現象のメカニズム
を模式的に示したものである。脱硫剤吹込みノズル11
の外周面に、水滴14が生成されると、図7(a)およ
び(b)で示したように、小さな巻込み渦21によって
、脱硫剤吹込みノズル11内面に水滴14が巻き込まれ
易くなり、これに脱硫剤5や排ガス中の燃焼灰などが付
着し、スラリ15化〔図7(c)〕すると共に乾燥して
固化〔図7(d)〕される。いったんこれが生成される
と、渦が生じ易くなり、ますます水滴14が巻き込まれ
、付着固化した脱硫剤13が成長する〔図7(e),(
f)〕。このため、脱硫剤吹込みノズル11の孔が狭く
なり、脱硫剤5のスムーズな導入が阻害され、極端な場
合にはノズルの閉塞にまで至る場合もあり、排ガスの脱
硫処理に支障をきたす。したがって、こうしたノズルの
閉塞問題の起こらない脱硫剤吹込みノズル11の設計が
要望されていた。When slaked lime powder is introduced as a desulfurizing agent under such conditions, the desulfurizing agent immediately adheres to the desulfurizing agent injection nozzle and hardens, and deposits gradually accumulate in layers. That is, FIGS. 7A to 7F schematically show the mechanism of the desulfurization agent adhesion phenomenon caused by dew condensation on the outer peripheral surface of the desulfurization agent injection nozzle. Desulfurizing agent injection nozzle 11
When water droplets 14 are generated on the outer circumferential surface of the desulfurizing agent blowing nozzle 11, the water droplets 14 are easily drawn into the inner surface of the desulfurizing agent injection nozzle 11 by the small entrained vortex 21, as shown in FIGS. 7(a) and 7(b). The desulfurizing agent 5 and combustion ash in the exhaust gas adhere to this, forming a slurry 15 [FIG. 7(c)] and drying and solidifying [FIG. 7(d)]. Once this is generated, vortices are likely to be generated, water droplets 14 are increasingly drawn in, and the attached and solidified desulfurization agent 13 grows [Fig. 7(e), (
f)]. For this reason, the hole of the desulfurizing agent injection nozzle 11 becomes narrow, preventing the smooth introduction of the desulfurizing agent 5, and in extreme cases, the nozzle may become clogged, which impedes the desulfurizing process of the exhaust gas. Therefore, it has been desired to design a desulfurizing agent injection nozzle 11 that does not cause such nozzle clogging problems.
【0009】本発明の目的は、上記従来技術における問
題点を解消するものであって、ボイラ等の燃焼炉の煙道
または脱硫塔内に脱硫剤を導入して、排ガス中のSOx
やHClなどの酸性有害物質と反応させて除去する排ガ
ス浄化設備の脱硫剤吹込み装置において、脱硫剤吹込み
ノズルの外周面の結露による脱硫剤の詰まりを容易に防
止することができる構造が簡単で安価な脱硫剤吹込み装
置を提供することにある。An object of the present invention is to solve the above-mentioned problems in the prior art, and to reduce SOx in exhaust gas by introducing a desulfurizing agent into the flue of a combustion furnace such as a boiler or into a desulfurizing tower.
In the desulfurizing agent injection device of exhaust gas purification equipment, which removes acidic hazardous substances such as chlorine and HCl by reaction, the structure is simple and can easily prevent the desulfurizing agent from clogging due to dew condensation on the outer circumferential surface of the desulfurizing agent injection nozzle. The purpose of the present invention is to provide an inexpensive desulfurizing agent injection device.
【0010】0010
【課題を解決するための手段】上述したごとく、従来の
脱硫剤吹込みノズルの問題点を解消するためには、■脱
硫剤を供給するノズルの内面を加熱して結露を防止する
温度以上に保持するか、または■付着固化した脱硫剤を
機械的に除去する必要がある。しかし、実際に上記■の
方法は加熱手段が複雑となり、また上記■の方法は運転
中では機械的に除去する操作が困難であるので、本発明
は脱硫剤吹込みノズルの形状を改良し、ノズル外周面に
結露した水分がノズル内面に引き込まれない特定の形状
の脱硫剤吹込みノズルとすることによって、脱硫剤によ
る目詰まりの問題を解決するものである。[Means for solving the problem] As mentioned above, in order to solve the problems of the conventional desulfurizing agent injection nozzle, it is necessary to heat the inner surface of the nozzle that supplies the desulfurizing agent to a temperature higher than that required to prevent condensation. It is necessary to either retain or mechanically remove the attached and hardened desulfurizing agent. However, in practice, method (1) requires a complicated heating means, and method (2) is difficult to mechanically remove during operation, so the present invention improves the shape of the desulfurizing agent injection nozzle, The problem of clogging caused by the desulfurizing agent is solved by providing a desulfurizing agent injection nozzle with a specific shape that prevents moisture condensed on the outer peripheral surface of the nozzle from being drawn into the inner surface of the nozzle.
【0011】本発明の脱硫剤吹込み装置において、脱硫
剤吹込みノズルの先端部に、緩やかに断面を拡大させた
末広がりのテーパ状ノズル(円筒)部材を設け、該テー
パ状ノズル部材のノズル部の口径をD1、テーパ状ノズ
ル部材の先端部の口径をD2、広がり角度(テーパ角度
)をθとするとき、D1/D2≧0.5およびθ≦7度
を、同時に満足する形状にノズル設計を行うことにより
、本発明の目的を達成することができる。In the desulfurizing agent blowing device of the present invention, a tapered nozzle (cylindrical) member with a gradually enlarged cross section is provided at the tip of the desulfurizing agent blowing nozzle, and a nozzle portion of the tapered nozzle member is provided. The nozzle is designed in a shape that simultaneously satisfies D1/D2≧0.5 and θ≦7 degrees, where D1 is the aperture of the tapered nozzle member, D2 is the aperture of the tip of the tapered nozzle member, and θ is the divergence angle (taper angle). By doing so, the object of the present invention can be achieved.
【0012】そして、D2/D1の値が2よりも大きく
なり、かつθが7度を超えるとテーパ状ノズル部材の末
広がり部の傾斜が急峻となり、テーパ状ノズル先端の拡
大部で小さな渦流が生じ易くなって、ノズルの外周面で
結露した水滴がノズルの内面に引き込まれ、これに脱硫
剤が付着して固化し、これが積層されノズル閉塞を引き
起こすので好ましくない。[0012] When the value of D2/D1 becomes larger than 2 and θ exceeds 7 degrees, the inclination of the end widening part of the tapered nozzle member becomes steep, and a small vortex is generated at the widening part of the tapered nozzle tip. This is undesirable because water droplets condensing on the outer circumferential surface of the nozzle are drawn into the inner surface of the nozzle, where the desulfurizing agent adheres and solidifies, causing the nozzle to become clogged.
【0013】[0013]
【作用】脱硫剤吹込みノズルの閉塞の原因としては、脱
硫剤の吹き出し部の流速が高いため、ノズル先端部で渦
流が発生し、この渦流にノズル外周部の水分および吹き
出す脱硫剤が巻き込まれて、しだいに脱硫剤吹込みノズ
ル内面に付着し成長してゆくためである。したがって、
ノズル断面がゆるやかに拡大する末広がりのテーパ状ノ
ズルとなし、テーパ状ノズル内での脱硫剤の流れが乱流
とならない程度の低流速にすれば、テーパ状ノズル先端
部における渦流の発生が抑制されるのでノズル外周面に
結露した水分がノズル内面に引き込まれ、脱硫剤が付着
固化することによるノズルの閉塞の問題は解決される。[Operation] The cause of blockage of the desulfurizing agent injection nozzle is that the flow velocity at the desulfurizing agent blowing part is high, so a vortex is generated at the tip of the nozzle, and the water on the outer periphery of the nozzle and the blown desulfurizing agent are caught up in this vortex. This is because the desulfurizing agent gradually adheres to the inner surface of the desulfurizing agent injection nozzle and grows. therefore,
If the cross-section of the nozzle is a tapered nozzle that gradually expands toward the end, and if the flow rate of the desulfurizing agent in the tapered nozzle is kept low enough to prevent turbulence, the generation of vortices at the tip of the tapered nozzle can be suppressed. Therefore, moisture condensed on the outer circumferential surface of the nozzle is drawn into the inner surface of the nozzle, and the problem of nozzle clogging caused by adhesion and solidification of the desulfurizing agent is solved.
【0014】[0014]
【実施例】以下に本発明の実施例を挙げ、図面を用いて
さらに詳細に説明する。EXAMPLES Examples of the present invention will be described below in more detail with reference to the drawings.
【0015】図1は、本発明の脱硫剤吹込み装置を用い
た排ガス浄化装置の構成を示す系統図である。図におい
て、ボイラ1には石炭焚き、重油焚き等があり、この燃
焼排ガス2は、硫黄化合物(SO2など)や燃焼灰を含
んだまま下流方向に流れる。途中、エアヒータ3で熱交
換され、その下流の煙道6に、水噴霧ノズル12および
脱硫剤吹込みノズル11が設けられ、ここで一次的な脱
硫反応が行われる。さらに、排ガス2は脱硫塔4に入り
、ここで再度水噴霧することによって脱硫反応を完結さ
せ、集塵装置8で捕集し廃棄処理すると共に、煙突9か
らはクリーンな排ガスが大気中に放出される。FIG. 1 is a system diagram showing the configuration of an exhaust gas purification device using the desulfurizing agent injection device of the present invention. In the figure, the boiler 1 includes a coal-fired boiler, a heavy oil-fired boiler, and the like, and the combustion exhaust gas 2 flows downstream while containing sulfur compounds (SO2, etc.) and combustion ash. On the way, heat is exchanged with the air heater 3, and a water spray nozzle 12 and a desulfurization agent injection nozzle 11 are provided in the flue 6 downstream thereof, where a primary desulfurization reaction is performed. Furthermore, the exhaust gas 2 enters the desulfurization tower 4, where it is sprayed with water again to complete the desulfurization reaction, collected by the dust collector 8, and disposed of, and clean exhaust gas is released into the atmosphere from the chimney 9. be done.
【0016】本実施例においては、脱硫剤として消石灰
の粉末を用い、石炭焚きボイラの排ガスを脱硫処理する
場合について説明する。In this embodiment, a case will be described in which slaked lime powder is used as a desulfurizing agent to desulfurize exhaust gas from a coal-fired boiler.
【0017】図1において、ボイラ1からの排ガス2は
、エアヒータ3で温度が下げられ、その下流の煙道6で
水噴霧ノズル12より水を噴霧し、脱硫剤吹込みノズル
11から噴出される脱硫剤5に水を添加する。さらに、
脱硫塔4でも水噴霧されて水が添加される。このような
水添加処理がなされた脱硫剤5は、排ガス中のSO2な
どの酸性有害物質と反応し、反応した脱硫剤5は排ガス
2中の灰とともに集塵装置8で捕集され廃棄される。脱
硫剤5を吹き込む際に、煙道6または脱硫塔4内に水を
噴霧して供給するが、これは排ガス2の温度を下げ、か
つ湿度を上げることによって脱硫反応率の向上をはかる
ものである。In FIG. 1, the temperature of exhaust gas 2 from a boiler 1 is lowered by an air heater 3, water is sprayed from a water spray nozzle 12 in a flue 6 downstream thereof, and is jetted from a desulfurizing agent injection nozzle 11. Water is added to the desulfurizing agent 5. moreover,
Water is also added to the desulfurization tower 4 by spraying water. The desulfurizing agent 5 subjected to such water addition treatment reacts with acidic harmful substances such as SO2 in the exhaust gas, and the reacted desulfurizing agent 5 is collected together with the ash in the exhaust gas 2 by a dust collector 8 and disposed of. . When the desulfurization agent 5 is injected, water is sprayed and supplied into the flue 6 or the desulfurization tower 4, but this is intended to improve the desulfurization reaction rate by lowering the temperature of the exhaust gas 2 and increasing the humidity. be.
【0018】このとき、脱硫剤吹込みノズル11は水噴
霧によって冷却され、また、脱硫剤5を気流搬送するキ
ャリアガスによっても冷却されるので、水分がノズル外
周面に結露した状態で付着し、これがノズル内面に浸透
する。これに、脱硫剤5である消石灰の粉末を導入する
と、たちまち脱硫剤がノズル内面に付着して固化し、こ
れがしだいに積層されてノズルが閉塞状態になる場合が
ある。このため、図2(a)〜(c)に示したように、
ノズル先端部の断面を緩やかに拡大させた末広がりのテ
ーパ状ノズル部材(ベンチュリイ管状)16を、脱硫剤
吹込みノズル11の先端部に取り付ける。すなわち、こ
のときテーパ状ノズル部材16のノズル部の口径D1と
テーパ状ノズル部材16の先端部の口径D2との関係を
、D1/D2≧0.5となし、ノズルの広がり角度(テ
ーパ角度)θを7°以下(テーパ状ノズル部材16の先
端部における角度も同じとする)とした。これは、ベン
チュリ管の末広がり部〔図2(b)〕のようにして、排
ガス2の進行方向に対し逆方向の渦が生じないような関
係を保つことが必要である。これがもし、D2/D1≫
2(D1/D2≪0.5),θ≫7°のように極端に広
がれば、図2(c)に示すように巻込み渦21がテーパ
状ノズル部材16の拡大部で発生し、結露した水滴14
が引き込まれ易くなるし、また逆にテーパ角度θが小さ
く細長いノズル形状では渦の抑制の効果が低下する。以
上のことから本実施例におけるテーパ状ノズル部材16
は、1>D1/D2≧0.5,3°<θ<7°を同時に
満足させるノズル形状とした。したがって、その先端部
はかなりの鋭角となり、ノズル部の外周面の湿り(水滴
)がここで吹き飛ばされ、水分がノズルの内面に回り込
むことがなくなり、ノズルの内面は常に乾燥した状態に
おかれているので、ノズル内および先端部近傍における
脱硫剤5の付着固化現象は生じない。At this time, the desulfurizing agent injection nozzle 11 is cooled by the water spray and is also cooled by the carrier gas that carries the desulfurizing agent 5 in airflow, so that moisture adheres to the outer peripheral surface of the nozzle in the form of dew. This penetrates into the inner surface of the nozzle. When slaked lime powder, which is the desulfurizing agent 5, is introduced, the desulfurizing agent immediately adheres to the inner surface of the nozzle and solidifies, and the desulfurizing agent is gradually piled up, which may cause the nozzle to become blocked. Therefore, as shown in FIGS. 2(a) to 2(c),
A tapered nozzle member (Venturi tube shape) 16 whose cross section at the tip of the nozzle is gradually enlarged is attached to the tip of the desulfurizing agent injection nozzle 11 . That is, at this time, the relationship between the aperture D1 of the nozzle portion of the tapered nozzle member 16 and the aperture D2 of the tip end of the tapered nozzle member 16 is set as D1/D2≧0.5, and the nozzle spread angle (taper angle) θ was set to 7° or less (the angle at the tip of the tapered nozzle member 16 is also the same). It is necessary to maintain a relationship in which a vortex in the opposite direction to the traveling direction of the exhaust gas 2 is not generated, as in the divergent part of the Venturi tube [FIG. 2(b)]. If this is D2/D1≫
2 (D1/D2≪0.5), θ≫7°, an entrainment vortex 21 is generated at the enlarged part of the tapered nozzle member 16 as shown in FIG. 2(c), and dew condensation occurs. water droplets 14
On the other hand, if the taper angle θ is small and the nozzle has an elongated shape, the effect of suppressing the vortices is reduced. From the above, the tapered nozzle member 16 in this embodiment
The nozzle shape was such that 1>D1/D2≧0.5 and 3°<θ<7° were satisfied at the same time. Therefore, the tip has a fairly acute angle, and the moisture (water droplets) on the outer circumferential surface of the nozzle is blown away, preventing moisture from entering the inner surface of the nozzle, and the inner surface of the nozzle is always kept dry. Therefore, the adhesion and solidification phenomenon of the desulfurizing agent 5 inside the nozzle and near the tip does not occur.
【0019】このように、脱硫剤導入管の先端部に上記
のテーパ状ノズル部材16を設けることにより、水分(
結露水など)の浸透がなくなり脱硫剤の付着固化が防止
できる。したがって、連続的に脱硫反応を継続すること
ができ、かつ脱硫反応効率も一段と向上する。As described above, by providing the above-mentioned tapered nozzle member 16 at the tip of the desulfurizing agent introduction pipe, moisture (
This prevents the penetration of condensed water, etc., and prevents the desulfurization agent from adhering and solidifying. Therefore, the desulfurization reaction can be continued continuously, and the desulfurization reaction efficiency is further improved.
【0020】上記の実施例において例示した脱硫剤導入
管の先端部に設ける末広がりのテーパ状ノズル部材は、
所定の広がり角度でテーパ状に拡大した形状の脱硫剤吹
込みノズルを例示したが、この他、例えば図3に示すよ
うなラッパ状に広がる断面を持つラッパ状ノズル部材1
7とした場合においても、脱硫剤吹込みノズルとして脱
硫剤の詰まりを防止することができる。このようにラッ
パ状に広げると、これに沿って脱硫剤が流れるので、脱
硫剤の分散効果も向上し脱硫反応の促進にも寄与するこ
とになる。[0020] The tapered nozzle member that widens toward the end provided at the tip of the desulfurizing agent introduction pipe exemplified in the above embodiments is as follows:
Although the desulfurizing agent blowing nozzle has been shown as an example of a desulfurizing agent injection nozzle that has a tapered shape that expands at a predetermined expansion angle, it is also possible to use a trumpet-shaped nozzle member 1 that has a trumpet-shaped cross section as shown in FIG. 3, for example.
7, it is possible to prevent clogging of the desulfurizing agent as a desulfurizing agent injection nozzle. When spread out in a trumpet shape, the desulfurizing agent flows along this, which improves the dispersion effect of the desulfurizing agent and contributes to promoting the desulfurization reaction.
【0021】図4は、テーパ状またはラッパ状ノズルの
内面の部分に耐摩耗材18を張り付け、脱硫剤による摩
耗を防止する構造のものである。これにより、ノズルの
長寿命が期待できる。FIG. 4 shows a structure in which a wear-resistant material 18 is attached to the inner surface of a tapered or trumpet-shaped nozzle to prevent wear caused by the desulfurizing agent. As a result, a long life of the nozzle can be expected.
【0022】[0022]
【発明の効果】本発明の脱硫剤吹込み装置は以下に示す
優れた効果があるので、排ガスの脱硫設備において、長
期にわたり連続して高い脱硫反応を安定して維持するこ
とができる。Effects of the Invention The desulfurizing agent injection device of the present invention has the following excellent effects, so that a high desulfurization reaction can be stably maintained continuously over a long period of time in exhaust gas desulfurization equipment.
【0023】(1)脱硫剤導入管の先端部に、設定の広
がり角度を有するテーパ状またはラッパ状に拡大したノ
ズル部材を設けることにより、ノズル先端部における渦
流の発生が抑制され、ノズル外周面に結露した水分の引
き込みが生じないので、ノズル内面部への消石灰などの
脱硫剤粉末の付着固化が防止できる。(1) By providing a tapered or trumpet-shaped enlarged nozzle member with a predetermined widening angle at the tip of the desulfurizing agent introduction pipe, the generation of vortices at the nozzle tip is suppressed, and the outer peripheral surface of the nozzle is Since no condensed water is drawn in, it is possible to prevent desulfurizing agent powder such as slaked lime from adhering to the inner surface of the nozzle and hardening.
【0024】(2)テーパ状またはラッパ状に拡大した
ノズル部材の先端部の鋭角の部分で、結露した水分など
が吹き飛ばされ、ノズル内面に水分が浸透しない。した
がって、常に乾燥した状態で脱硫剤粉末の噴霧を行うこ
とかできる。(2) Condensed moisture is blown away at the acute-angled portion of the tip of the nozzle member, which is enlarged in a tapered or trumpet shape, so that moisture does not penetrate into the inner surface of the nozzle. Therefore, the desulfurizing agent powder can always be sprayed in a dry state.
【0025】(3)脱硫剤導入管の先端部に設ける本発
明の脱硫剤吹込みノズルは構造が簡単であり、容易に設
計製作できるので設備費が安価となる。(3) The desulfurizing agent injection nozzle of the present invention provided at the tip of the desulfurizing agent introduction pipe has a simple structure and can be easily designed and manufactured, resulting in low equipment costs.
【図1】本発明の実施例で例示した脱硫剤吹込みノズル
を有する排ガス脱硫装置を用いたボイラ全体の構成を示
す系統図。FIG. 1 is a system diagram showing the overall configuration of a boiler using an exhaust gas desulfurization apparatus having a desulfurization agent injection nozzle exemplified in an embodiment of the present invention.
【図2】本発明の実施例で例示したテーパ状ノズル部材
の構成の一例を示す模式図。FIG. 2 is a schematic diagram showing an example of the configuration of a tapered nozzle member illustrated in an example of the present invention.
【図3】本発明の実施例で例示したラッパ状ノズル部材
の構成の一例を示す模式図。FIG. 3 is a schematic diagram showing an example of the configuration of a trumpet-shaped nozzle member illustrated in an example of the present invention.
【図4】本発明の実施例で例示したテーパ状部またはラ
ッパ状部に耐摩耗材を張り付けたノズル部材の構成の一
例を示す模式図。FIG. 4 is a schematic diagram showing an example of the configuration of a nozzle member in which a wear-resistant material is attached to a tapered portion or a trumpet-shaped portion illustrated in an example of the present invention.
【図5】従来の排ガス脱硫装置を備えたボイラ全体の構
成を示す模式図。FIG. 5 is a schematic diagram showing the overall configuration of a boiler equipped with a conventional exhaust gas desulfurization device.
【図6】従来の脱硫剤吹込みノズルおよび水噴霧ノズル
の構成を示す模式図。FIG. 6 is a schematic diagram showing the configuration of a conventional desulfurizing agent blowing nozzle and a water spray nozzle.
【図7】従来の脱硫剤吹込みノズル先端部における脱硫
剤粉末の付着固化現象のメカニズムを示す模式図。FIG. 7 is a schematic diagram showing the mechanism of adhesion and solidification of desulfurization agent powder at the tip of a conventional desulfurization agent injection nozzle.
1…ボイラ
2…排ガス3…エアヒータ
4…脱硫塔5…脱硫剤
6…煙道7…スラリ
8…集塵装
置9…煙突
10…脱硫剤導入管11…脱硫剤吹込みノズル
12…水噴霧ノズル13…付着固化し
た脱硫剤 14…水滴15…スラリ
16…テーパ状
ノズル部材
17…ラッパ状ノズル部材 18…耐摩
耗材19…巻込み渦1...Boiler
2...Exhaust gas 3...Air heater
4...Desulfurization tower 5...Desulfurization agent
6... Flue 7... Slurry
8... Dust collector 9... Chimney
10...Desulfurizing agent introduction pipe 11...Desulfurizing agent injection nozzle 12...Water spray nozzle 13...Desulfurizing agent adhered and solidified 14...Water droplets 15...Slurry
16...Tapered nozzle member 17...Trumpet-shaped nozzle member 18...Wear-resistant material 19...Involved vortex
Claims (2)
入して、排ガス中に含まれる酸性有害物質を除去する排
ガス浄化設備の脱硫剤吹込み装置において、該脱硫剤吹
込み装置は、脱硫剤の導入管の先端部に、ノズル断面を
緩やかに拡大させた末広がり状のノズル部材を設け、該
ノズル部材は、ノズル部の口径をD1、ノズル先端部の
口径をD2、ノズルの広がり角度をθとするとき、D1
/D2≧0.5およびθ≦7度を同時に満足する形状と
することを特徴とする脱硫剤吹込み装置。Claim 1: A desulfurization agent injection device for exhaust gas purification equipment that introduces a desulfurization agent into a flue of a combustion furnace or into a desulfurization tower to remove acidic harmful substances contained in exhaust gas, the desulfurization agent injection device In this method, a nozzle member with a gradually expanding nozzle cross section is provided at the tip of the desulfurizing agent introduction pipe, and the nozzle member has a diameter of D1, a diameter of the tip of the nozzle, D2, and a diameter of D2. When the spread angle is θ, D1
A desulfurizing agent injection device characterized by having a shape that simultaneously satisfies /D2≧0.5 and θ≦7 degrees.
材は、テーパ状に断面を拡大させた円筒部材もしくはラ
ッパ状に断面を拡大させた円筒部材よりなることを特徴
とする脱硫剤吹込み装置。2. The desulfurizing agent blowing device according to claim 1, wherein the nozzle member which is flared toward the end is made of a cylindrical member whose cross section is enlarged in a tapered shape or a cylindrical member whose cross section is enlarged in a trumpet shape. .
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3030373A JPH04358518A (en) | 1991-02-25 | 1991-02-25 | Desulfurizing agent blowing device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3030373A JPH04358518A (en) | 1991-02-25 | 1991-02-25 | Desulfurizing agent blowing device |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04358518A true JPH04358518A (en) | 1992-12-11 |
Family
ID=12302078
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP3030373A Pending JPH04358518A (en) | 1991-02-25 | 1991-02-25 | Desulfurizing agent blowing device |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH04358518A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH08141349A (en) * | 1994-11-17 | 1996-06-04 | Mitsubishi Heavy Ind Ltd | Gas/liquid contact device |
WO1999045584A1 (en) * | 1998-03-06 | 1999-09-10 | Tokyo Electron Limited | Processing apparatus |
US8075858B1 (en) * | 2009-10-07 | 2011-12-13 | White Cliff Technologies, LLC | Trumpet shaped element and process for minimizing solid and gaseous pollutants from waste off-gasses and liquid streams |
-
1991
- 1991-02-25 JP JP3030373A patent/JPH04358518A/en active Pending
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH08141349A (en) * | 1994-11-17 | 1996-06-04 | Mitsubishi Heavy Ind Ltd | Gas/liquid contact device |
WO1999045584A1 (en) * | 1998-03-06 | 1999-09-10 | Tokyo Electron Limited | Processing apparatus |
EP1069603A1 (en) * | 1998-03-06 | 2001-01-17 | Tokyo Electron Limited | Processing apparatus |
US6733620B1 (en) | 1998-03-06 | 2004-05-11 | Tokyo Electron Limited | Process apparatus |
US8075858B1 (en) * | 2009-10-07 | 2011-12-13 | White Cliff Technologies, LLC | Trumpet shaped element and process for minimizing solid and gaseous pollutants from waste off-gasses and liquid streams |
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