JPH0566009A - Exhaust gas temperature reducer and reducing method thereof - Google Patents
Exhaust gas temperature reducer and reducing method thereofInfo
- Publication number
- JPH0566009A JPH0566009A JP3255856A JP25585691A JPH0566009A JP H0566009 A JPH0566009 A JP H0566009A JP 3255856 A JP3255856 A JP 3255856A JP 25585691 A JP25585691 A JP 25585691A JP H0566009 A JPH0566009 A JP H0566009A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- spray
- gas temperature
- angle
- temperature
- 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
- 238000000034 method Methods 0.000 title claims description 7
- 239000003638 chemical reducing agent Substances 0.000 title description 5
- 239000007921 spray Substances 0.000 claims abstract description 124
- 239000002245 particle Substances 0.000 claims abstract description 36
- 230000007423 decrease Effects 0.000 claims abstract description 13
- 238000005507 spraying Methods 0.000 claims description 34
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 13
- 239000000920 calcium hydroxide Substances 0.000 claims description 13
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 13
- 235000011116 calcium hydroxide Nutrition 0.000 claims description 13
- 239000002002 slurry Substances 0.000 claims description 13
- 239000004572 hydraulic lime Substances 0.000 claims description 7
- 238000001514 detection method Methods 0.000 claims description 6
- 230000003247 decreasing effect Effects 0.000 claims 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 35
- 239000002699 waste material Substances 0.000 description 19
- 239000000428 dust Substances 0.000 description 18
- 238000010586 diagram Methods 0.000 description 6
- 238000001704 evaporation Methods 0.000 description 5
- 230000008020 evaporation Effects 0.000 description 5
- 239000013505 freshwater Substances 0.000 description 3
- 238000005260 corrosion Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000012717 electrostatic precipitator Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
Landscapes
- Chimneys And Flues (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本件発明は、廃棄物焼却炉等の排
ガスの減温に使用されるものであり、集塵装置のガス入
り口側に設置する水噴射式ガス減温装置と、これを利用
したガス減温方法の改良に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is used for reducing the temperature of exhaust gas from a waste incinerator and the like, and a water injection type gas temperature reducing device installed on the gas inlet side of a dust collector, The present invention relates to improvement of the gas temperature reduction method used.
【0002】[0002]
【従来の技術】従来から廃棄物焼却炉等では、排ガス処
理用に電気集塵機が広く利用されてきた。ところが、近
年排ガス温度が約300℃前後になると、電気集塵機内
に於いてダイオキシンの再合成が起こることが判明し、
これにより集塵機へ導入する排ガスの温度を150℃〜
250℃程度に減温する必要が生じてきた。そのため、
多くの廃棄物焼却炉では集塵装置のガス入口側に、排ガ
ス内へ水又は消石灰スラリーを噴霧してガス温度を低減
するようにした半乾式ガス減温装置を設置し、減温装置
出口側のガス温度によって噴霧水量を調整することによ
り、集塵装置へ導入するガスの温度を所定温度範囲に自
動制御するようにしている。2. Description of the Related Art Conventionally, in dust incinerators and the like, an electric dust collector has been widely used for treating exhaust gas. However, it has become clear that the dioxin re-synthesis occurs in the electrostatic precipitator when the exhaust gas temperature reaches around 300 ° C in recent years.
As a result, the temperature of the exhaust gas introduced into the dust collector is 150 ° C to
It has become necessary to reduce the temperature to about 250 ° C. for that reason,
In many waste incinerators, a semi-dry gas temperature reducer that sprays water or slaked lime slurry into the exhaust gas to reduce the gas temperature is installed on the gas inlet side of the dust collector, and the temperature reducer outlet side. By adjusting the amount of spray water according to the gas temperature, the temperature of the gas introduced into the dust collector is automatically controlled within a predetermined temperature range.
【0003】前記従前の半乾式ガス減温装置は比較的容
易にガス温度を減温することができ、優れた実用的効用
を有するものである。しかし、当該装置にも解決すべき
多くの問題が残されている。先ず第1の問題は、噴霧す
る水量が多くなると、噴霧粒子密度が高くなって排ガス
との接触効率が悪化し、その結果、噴霧粒子がガスと混
合して完全に蒸発するまでに長時間を要することにな
り、減温装置が大型化すると云う点である。即ち、都市
ごみ焼却炉の場合には、ごみの低位発熱量がごみ質によ
って大きく変動する(例えば1500kcal/kgの
最低ごみ質から3000kcal/kgの最高ごみ
質)。従って、一般にガス減温装置の設計に於いては、
最高ごみ質を焼却する場合を基準として設計を行い、必
要とする最大噴霧水量に応じた数量の噴霧パターンが一
定の噴霧ノズルを設置するようにしている。ところが、
焼却すべきごみのごみ質が悪く、必要とする噴霧水量が
少ない場合には、ガス量が少ないこととも相俟って噴霧
パターンPは図5に示す如き状態となり、その噴霧粒子
密度Qは比較的低くなる。その結果、排ガスCと噴霧粒
子との接触効率が高くなると共に、噴霧パターンPの長
さ寸法Xが短くなる。尚、図5に於いてAは噴霧ノズ
ル、Bは噴霧水、Cは排ガスである。これに対して、焼
却するごみの低位発熱量が高い高質ごみの場合には、必
然的に噴霧水量が多くなる。ところが、前述の如く噴霧
パターンが一定のノズルを使用しているため、噴霧ノズ
ルAの噴出角度αは噴霧水量の大小に拘わらずほぼ一定
となる。そのため、噴霧粒子のパターンP´はガス量が
増大することとも相俟って図6に示す如き状態となり、
噴霧粒子密度Q´が図5の場合に比較して大となり、噴
霧粒子と排ガスCとの接触効率が悪化すると共に、噴霧
パターンP´の長さ寸法X´が増大することになる。The above-mentioned conventional semi-dry gas temperature reducer can reduce the gas temperature relatively easily and has excellent practical utility. However, many problems remain to be solved in the device. The first problem is that when the amount of water to be sprayed is large, the density of spray particles becomes high and the contact efficiency with exhaust gas deteriorates. As a result, it takes a long time for the spray particles to mix with the gas and completely evaporate. This means that the temperature reducing device becomes large in size. That is, in the case of the municipal waste incinerator, the lower calorific value of the waste greatly varies depending on the waste quality (for example, the minimum waste quality of 1500 kcal / kg to the maximum waste quality of 3000 kcal / kg). Therefore, in general, when designing a gas cooler,
The design is based on the case of incinerating the highest quality waste, and the spray nozzles are installed with a constant spray pattern in a quantity corresponding to the maximum spray water volume required. However,
When the quality of the waste to be incinerated is poor and the required amount of spray water is small, the amount of gas is small, and the spray pattern P becomes a state as shown in FIG. Will be low. As a result, the contact efficiency between the exhaust gas C and the spray particles becomes high, and the length dimension X of the spray pattern P becomes short. In FIG. 5, A is a spray nozzle, B is spray water, and C is exhaust gas. On the other hand, in the case of high-quality waste that has a low calorific value of the waste to be incinerated, the amount of spray water will inevitably increase. However, since the nozzles having a constant spray pattern are used as described above, the ejection angle α of the spray nozzle A is substantially constant regardless of the amount of spray water. Therefore, the pattern P ′ of the sprayed particles becomes a state as shown in FIG. 6 together with the increase of the gas amount,
The spray particle density Q'becomes larger than in the case of FIG. 5, the contact efficiency between the spray particles and the exhaust gas C is deteriorated, and the length dimension X'of the spray pattern P'is increased.
【0004】第2の問題は、ガス流量が少なくなると、
噴霧粒子が蒸発を完了するまでに移動する水平方向距離
が増大し、その結果、ガス減温装置の噴霧ノズルから側
壁までの必要寸法が増大して装置の内径が大きくなると
いう点である。即ち、前述の如く、噴霧粒子の蒸発効率
を上げるためには、噴霧ノズルの噴霧パターンPを図7
の如き狭角噴霧から図8のような広角噴霧にし、噴霧粒
子密度Qを小さくして排ガスとの接触面積S(投影面
積)を大きくすればよい。ところが、ごみ焼却炉では前
述の如くごみ質が大きく変動するため、ガス流量も大き
く変動することになり、低質ごみの燃焼時やごみ焼却炉
の燃焼負荷を下げた時には、ガス流量が減少してガス流
速も低下する。また、噴霧ノズルAから噴出される噴霧
粒子の水平方向の噴出速度は、その噴出角度αがほぼ一
定であることからして、噴霧水量が多少変動してもほぼ
一定の値となる。その結果、焼却すべきごみが高質であ
ってガス流量が大きく、ガス流速dの場合には、噴霧粒
子が完全に蒸発をするまでに移動する距離fは、図9に
示す如く速度ベクトルgと同一方向となり、この時の必
要とする噴霧ノズルAから減温装置側壁までの水平距離
は、ほぼ寸法Lとなる。尚eは噴霧粒子の噴出速度であ
る。これに対して、ごみが低品質であってガス流量も少
なく、その結果、ガス流速d´が遅い場合には、噴霧粒
子の移動方向は図10に示す如くベクトルg´と同一方
向となり、噴霧粒子が完全に蒸発をするまでの移動距離
fを図9の場合と同一とすると、必要とする噴霧ノズル
Aから減温装置側壁までの水平距離L´はL+Laとな
る。即ち、ガス流量が大となる場合に比較して、ノズル
Aから側壁までの水平距離L´は寸法Laだけ大きくす
る必要がある。The second problem is that when the gas flow rate decreases,
The point is that the horizontal distance traveled by the spray particles to complete evaporation is increased, resulting in an increase in the required size from the spray nozzle to the side wall of the gas cooler and an increase in the internal diameter of the device. That is, as described above, in order to increase the evaporation efficiency of the spray particles, the spray pattern P of the spray nozzle is set as shown in FIG.
The narrow-angle spray as shown in FIG. 8 is changed to the wide-angle spray as shown in FIG. 8 to reduce the spray particle density Q and increase the contact area S (projected area) with the exhaust gas. However, in the waste incinerator, since the quality of the waste fluctuates greatly as described above, the gas flow rate also fluctuates greatly, and the gas flow rate decreases when burning low-quality waste or when reducing the combustion load of the waste incinerator. The gas flow rate also decreases. Further, the horizontal ejection speed of the spray particles ejected from the spray nozzle A becomes a substantially constant value even if the amount of spray water slightly fluctuates because the ejection angle α is substantially constant. As a result, when the waste to be incinerated is of high quality, the gas flow rate is large, and the gas flow rate is d, the distance f that the sprayed particles move to completely evaporate is as shown in FIG. The horizontal distance from the spray nozzle A to the side wall of the temperature reducer required at this time is approximately L. Note that e is the ejection velocity of the spray particles. On the other hand, when the dust is of low quality and the gas flow rate is small, and as a result, the gas flow velocity d ′ is slow, the moving direction of the spray particles is the same as the vector g ′ as shown in FIG. If the moving distance f until the particles are completely evaporated is the same as in the case of FIG. 9, the required horizontal distance L ′ from the spray nozzle A to the side wall of the temperature reducing device is L + La. That is, the horizontal distance L ′ from the nozzle A to the side wall needs to be increased by the dimension La as compared with the case where the gas flow rate is large.
【0005】上述の如く、従前の噴出角度αが一定の噴
霧ノズルAを使用する排ガス減温装置においては、理論
的には装置の高さを図6のX´及び側壁からノズルAま
での水平方向距離を図10のL´とすればよいが、実際
の減温装置の設計に於いては、蒸発が完了する前に噴霧
粒子が側壁へ衝突すると、排ガス内に含まれる酸性ガス
により側壁に激しい腐食が発生するため寸法的に十分な
る余裕を取る必要があり、塔径並びに塔高さの大きな装
置になるというのが現状である。As described above, in the conventional exhaust gas temperature reducing device using the spray nozzle A having a constant jet angle α, theoretically, the height of the device is X ′ in FIG. 6 and the horizontal from the side wall to the nozzle A. The direction distance may be set to L ′ in FIG. 10, but in the actual design of the temperature reducing device, if the sprayed particles collide with the side wall before the completion of evaporation, the acid gas contained in the exhaust gas causes the side wall to contact the side wall. Since severe corrosion occurs, it is necessary to secure a sufficient dimensional allowance, and the present situation is that the equipment will have a large tower diameter and tower height.
【0006】[0006]
【発明が解決しようとする課題】本発明は、従前のごみ
焼却炉等の排ガス減温装置に於ける上述の如き問題、即
ち、(イ)焼却すべきごみ等が高質で噴霧水量が増大す
ると、噴霧粒子と排ガスとの接触効率が低下して噴霧粒
子の完全蒸発までに時間がかかり、排ガス減温装置の高
さ寸法が大きくなること、及び(ロ)焼却すべきごみ等
が低質で排ガス量が減少(噴霧水量が減少)すると、噴
霧粒子の水平方向への移動距離が増大して排ガス減温装
置の内径寸法が大きくなること等の問題を解決せんとす
るものであり、噴霧水量やガス流量に応じて噴霧ノズル
の噴霧角度αを調整して噴霧パターンを変えることによ
り、装置の大幅な小形化を可能とした排ガス減温装置と
排ガス減温方法を提供するものである。DISCLOSURE OF THE INVENTION The present invention has the above-mentioned problems in the conventional exhaust gas temperature control devices for waste incinerators, that is, (a) the quality of waste to be incinerated is high and the amount of spray water increases. Then, the contact efficiency between the spray particles and the exhaust gas decreases, it takes time to completely evaporate the spray particles, the height dimension of the exhaust gas temperature control device becomes large, and (b) the waste to be incinerated is of low quality. When the amount of exhaust gas decreases (the amount of spray water decreases), the movement distance of the spray particles in the horizontal direction increases, and the problem that the inner diameter of the exhaust gas temperature control device increases, etc. will be solved. The present invention provides an exhaust gas temperature reducing device and an exhaust gas temperature reducing method that can significantly reduce the size of the device by adjusting the spray angle α of the spray nozzle according to the gas flow rate and changing the spray pattern.
【0007】[0007]
【課題を解決するための手段】本件装置発明は、排ガス
が流通する竪型のガス減温塔5と;ガス減温塔5内へ水
又は消石灰スラリーを噴霧すると共に、その噴出角度α
を調整自在とした噴霧装置7と;減温は排ガスの温度を
検出し、その検出信号により消石灰スラリーの噴霧量を
調節する排ガス温度制御装置10と;排ガスの熱量が増
えると前記噴出角度αを大に、また排ガスの熱量が減る
と噴出角度αを小にする噴霧パターン制御装置8とを発
明の基本構成とするものである。The present invention is directed to a vertical type gas temperature reducing tower 5 through which exhaust gas flows; and water or slaked lime slurry is sprayed into the gas temperature reducing tower 5 and its ejection angle α.
And an exhaust gas temperature control device 10 for detecting the temperature of the exhaust gas for temperature reduction and adjusting the spray amount of the slaked lime slurry by the detection signal; and the jet angle α when the heat amount of the exhaust gas increases. The spray pattern control device 8 that greatly reduces the jet angle α when the amount of heat of exhaust gas decreases is the basic configuration of the invention.
【0008】また、本件方法発明は、排ガスが流通する
ガス減温塔内へ噴霧装置により水又は消石灰スラリーを
噴霧して排ガスを減温する排ガス減温方法に於いて、排
ガス流量と排ガス温度を検出し、前記排ガス温度の検出
値により噴霧水又は消石灰スラリーの噴霧量を調整して
排ガス温度を制御すると共に、前記排ガス流量と排ガス
温度の検出値から排ガス熱量を演算し、排ガス熱量が増
えると前記噴霧装置からの噴霧粒子の噴出角度αを増す
方向に、また排ガス熱量が減少すると前記噴出角度αを
減らす方向に夫々制御することを発明の基本構成とする
ものである。Further, the method of the present invention is an exhaust gas temperature reducing method of spraying water or slaked lime slurry by a spraying device into a gas temperature reducing tower in which exhaust gas flows to reduce the temperature of the exhaust gas. Detected, while controlling the exhaust gas temperature by adjusting the spray amount of spray water or slaked lime slurry by the detected value of the exhaust gas temperature, the exhaust gas heat amount is calculated from the exhaust gas flow rate and the detected value of the exhaust gas temperature, when the exhaust gas heat amount increases The basic configuration of the invention is to control the spraying angle α of the sprayed particles from the spraying device so as to increase, and to control the spraying angle α to decrease when the heat quantity of exhaust gas decreases.
【0009】[0009]
【作用】排ガス減温装置内へ流入した排ガスは、ダスト
セパレータ内で粗粉塵を除去されたあと、ガス減温塔5
の下方から上方へ向かって流通する。ガス減温塔5の下
方に配設された噴霧装置7からは、温度検出器10aの
信号により開閉制御される弁10bを通して水等がガス
内へ噴霧され、これによって排ガス温度が所定値に保持
される。排ガスの流量及び温度から、排ガスの熱量が演
算され、この熱量の演算値が増大すると、噴霧パターン
制御装置8を介して噴霧装置7の噴出角度αが増大さ
れ、所謂広角噴霧の状態となる。これにより、噴霧粒子
が完全蒸発するまでの上方への移動距離が短縮される。
また、排ガス熱量の演算値が減少すると、噴霧パターン
制御装置8を介して噴出角度αが小さくされ、所謂狭角
噴霧の状態となる。これにより、噴霧粒子が完全蒸発す
るまでの水平方向への移動距離が短縮される。前記上方
並びに水平方向への噴霧粒子の移動距離が短縮されるこ
とにより、装置の小形化が可能となる。[Function] Exhaust gas that has flowed into the exhaust gas temperature reduction device is subjected to the removal of coarse dust in the dust separator, and then the gas temperature reduction tower 5
Flows from below to above. Water or the like is sprayed into the gas from a spraying device 7 arranged below the gas temperature reducing tower 5 through a valve 10b which is controlled to open and close by a signal from a temperature detector 10a, whereby the exhaust gas temperature is kept at a predetermined value. To be done. The heat quantity of the exhaust gas is calculated from the flow rate and the temperature of the exhaust gas, and when the calculated value of the heat quantity increases, the ejection angle α of the spray device 7 is increased via the spray pattern control device 8 and a so-called wide-angle spray state is established. This shortens the upward moving distance until the spray particles are completely evaporated.
Further, when the calculated value of the exhaust gas heat amount decreases, the ejection angle α is reduced via the spray pattern control device 8 and a so-called narrow-angle spray state is established. As a result, the moving distance in the horizontal direction until the spray particles are completely evaporated is shortened. By shortening the moving distance of the spray particles in the upward and horizontal directions, it is possible to downsize the device.
【0010】[0010]
【実施例】以下、図面に基づいて本発明の実施例を説明
する。図1は本発明に係る排ガス減温装置の系統図であ
り、図に於いて1は排ガス入口ダクト、2は排ガス出口
ダクト、3は集塵装置、4は排ガス減温装置、5はガス
減温塔、5aは整流板、6はダストセパレータ、6aは
ロータリーダンパ、7は噴霧装置、8は噴霧パターン制
御装置、9は噴出角度の調整駆動装置、9aはモータ、
9bはギヤ、9cはラックギヤ、10はガス温度制御装
置、10aは温度検出器、10bは噴霧水量制御弁、1
1はガス流量測定装置、12はガス熱量演算装置、Hは
高温排ガス、Haは低温排ガス、Wは噴霧水、A0は噴
霧用空気である。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a system diagram of an exhaust gas temperature reducing device according to the present invention, in which 1 is an exhaust gas inlet duct, 2 is an exhaust gas outlet duct, 3 is a dust collector, 4 is an exhaust gas temperature reducing device, and 5 is a gas reducing device. Hot tower, 5a is a current plate, 6 is a dust separator, 6a is a rotary damper, 7 is a spraying device, 8 is a spraying pattern control device, 9 is a jetting angle adjusting drive device, 9a is a motor,
9b is a gear, 9c is a rack gear, 10 is a gas temperature control device, 10a is a temperature detector, 10b is a spray water amount control valve, 1
Reference numeral 1 is a gas flow rate measuring device, 12 is a gas heat quantity calculating device, H is a high temperature exhaust gas, Ha is a low temperature exhaust gas, W is spray water, and A 0 is spray air.
【0011】本発明に係るガス減温装置4は、ダストセ
パレータ6を設けた竪形のガス減温塔5と、ダストセパ
レータ6を貫通してガス減温塔5内へノズル部を突出せ
しめた噴霧装置7と、噴霧装置7の噴霧粒子の噴出角度
αを調整する噴霧パターン制御装置8と、排ガスの温度
を制御する排ガス温度制御装置10等から構成されてい
る。The gas temperature reducing apparatus 4 according to the present invention has a vertical gas temperature reducing tower 5 provided with a dust separator 6, and a nozzle portion protruding through the dust separator 6 into the gas temperature reducing tower 5. The spray device 7 includes a spray pattern control device 8 for adjusting the spray angle α of spray particles of the spray device 7, an exhaust gas temperature control device 10 for controlling the temperature of exhaust gas, and the like.
【0012】前記噴霧装置7は、図2に示す如く、先端
部にノズルキャップ13を備え且つ側壁に噴霧用空気A
0の供給孔14aを設けた外管14と、外管14内へ同
芯状に挿入して左右方向へ移動自在に支持されると共
に、先端部に外管14の内方と連通する噴霧水Wの噴出
口15aを設けた内管15と、内管15の先端に固着さ
れてノズルキャップ13との間に噴霧水Wと噴霧用空気
A0の混合体の噴出口17を形成するノズルフレア16
と、内管移動レバー18aを揺動させることにより、ね
じ18bを介して内管15を左右方向へ移動させる内管
移動機構18等より形成されている。当該水噴霧装置7
は、内管15の基端部開口から噴霧水W又は消石灰スラ
リーが、また外管14から噴霧用空気A0が供給され、
微粒化された噴霧粒子が噴出口17から噴出される。こ
の時、内管移動用レバー18aを作動せしめて内管15
を左方向へ突出させると、微粒化された液滴がノズルフ
レア16のテーパ面に沿って円錐状に拡散し、図3に示
す如く噴霧水の噴出角度αが広角となる。また、逆に内
管15を右方向へ移動せしめて噴出口17の間隙を狭め
ると、微粒化された液滴はより高速で噴出されることに
なり、図4に示す如く内方部Eが真空状態となる。その
結果、噴出された液滴が内方部へ引き寄せられ、噴出角
度αが狭角となる。As shown in FIG. 2, the spraying device 7 has a nozzle cap 13 at its tip and spraying air A on its side wall.
The outer pipe 14 having the 0 supply hole 14a and the spray water that is inserted into the outer pipe 14 concentrically and is movably supported in the left-right direction and communicates with the inner side of the outer pipe 14 at its tip. A nozzle flare that forms an ejection port 17 of a mixture of spray water W and atomizing air A 0 between the inner pipe 15 provided with the ejection port 15a of W and the tip of the inner pipe 15 and is fixed to the nozzle cap 13. 16
The inner pipe moving mechanism 18 and the like move the inner pipe 15 in the left-right direction via the screw 18b by swinging the inner pipe moving lever 18a. The water spray device 7
Is supplied with spray water W or slaked lime slurry from the base end opening of the inner pipe 15, and spray air A 0 from the outer pipe 14,
The atomized spray particles are ejected from the ejection port 17. At this time, the inner pipe moving lever 18a is operated to operate the inner pipe 15
When is ejected to the left, the atomized droplets are diffused in a conical shape along the tapered surface of the nozzle flare 16 and the spray angle α of the spray water becomes wide as shown in FIG. On the contrary, when the inner tube 15 is moved to the right to narrow the gap of the ejection port 17, the atomized droplets are ejected at a higher speed, and the inner portion E is ejected as shown in FIG. It becomes a vacuum state. As a result, the ejected liquid droplets are attracted to the inner portion, and the ejection angle α becomes a narrow angle.
【0013】尚、本実施例では、本件発明者が先に開発
した特公昭60−27892号と同じ機構の噴霧装置7
を使用しているが、噴出角度αを変化して所謂噴霧パタ
ーンを調整できる噴霧装置であれば、如何なる構造のも
のであってもよい。また、本実施例ではねじ機構を利用
した内管移動機構18としているが、如何なる内管移動
機構18であってもよいことは勿論である。In this embodiment, the spraying device 7 having the same mechanism as the Japanese Patent Publication No. 60-27892 developed by the inventor of the present invention.
However, any structure may be used as long as it is a spray device capable of adjusting a so-called spray pattern by changing the jet angle α. Further, although the inner pipe moving mechanism 18 using the screw mechanism is used in the present embodiment, it goes without saying that any inner pipe moving mechanism 18 may be used.
【0014】前記噴霧パターン制御装置8は排ガス温度
検出器10aと、ガス流量測定装置11と、ガス熱量演
算装置12と、噴出角度αの調整駆動装置9等から構成
されており、後述する如く排ガスの検出温度と検出流量
から排ガス熱量が演算され、その演算値によって調整駆
動装置9が作動され、噴霧装置7の噴出角度αが調整さ
れる。The spray pattern control device 8 is composed of an exhaust gas temperature detector 10a, a gas flow rate measuring device 11, a gas calorific value calculation device 12, a drive device 9 for adjusting the ejection angle α, etc. The exhaust gas heat quantity is calculated from the detected temperature and the detected flow rate, and the adjustment drive device 9 is operated by the calculated value to adjust the ejection angle α of the spray device 7.
【0015】前記噴出角度αの調整駆動装置9はモータ
9aとギヤ9bとラック9c等から構成されており、噴
霧装置7の内管移動機構の内管移動用レバー18aへ一
端を軸支したラック9cにギヤ9bが噛合っており、当
該ギヤ9bをモータ9aにより回転することによりレバ
ー18aが作動され、これによって噴出角度αが調整さ
れる。The drive unit 9 for adjusting the ejection angle α is composed of a motor 9a, a gear 9b, a rack 9c, etc., and a rack whose one end is axially supported by an inner pipe moving lever 18a of an inner pipe moving mechanism of the spraying device 7. The gear 9b is meshed with the gear 9c, and the lever 18a is operated by rotating the gear 9b by the motor 9a, whereby the ejection angle α is adjusted.
【0016】前記ガス温度制御装置10は減温塔5の排
ガス出口側に設けた温度検出器10aと噴霧水量制御弁
10b等から形成されており、温度検出信号によって制
御弁10bを開閉制御することにより、低温排ガスHa
の温度が設定値に自動制御される。The gas temperature control device 10 is composed of a temperature detector 10a provided on the exhaust gas outlet side of the temperature reducing tower 5 and a spray water amount control valve 10b, and controls the opening / closing of the control valve 10b by a temperature detection signal. Due to the low temperature exhaust gas Ha
Temperature is automatically controlled to the set value.
【0017】次に、本発明による高温排ガスHの減温操
作について説明する。図1を参照して、ごみ焼却炉等か
ら排出された高温排ガスHは、排ガス入口ダクト1を通
してダクトセパレータ6内へ導入され、先ず排ガスH内
の粗ダストが除去される。その後排ガスHは、整流板5
aにより整流され乍らガス減温塔5内へ流入する。ま
た、回収された粗ダストはロータリーダンパ6aを通し
て適宜に排出される。一方、噴霧装置7の内管15内へ
は所定圧力の清水W(又は消石灰スラリー)が噴霧水量
制御弁10bを通して供給され、また噴霧用空気供給口
14aへは所定圧力の噴霧用空気A0が空気制御弁19
を通して供給される。これにより所定量の噴霧粒子がガ
ス減温塔5内へ噴出され、排ガスHと混合して蒸発する
ことにより、排ガスHが冷却される。Next, the operation of reducing the temperature of the high temperature exhaust gas H according to the present invention will be described. Referring to FIG. 1, high temperature exhaust gas H discharged from a refuse incinerator or the like is introduced into duct separator 6 through exhaust gas inlet duct 1, and coarse dust in exhaust gas H is first removed. After that, the exhaust gas H is rectified by the straightening plate 5.
It is rectified by a and flows into the gas temperature reduction tower 5. Further, the recovered coarse dust is appropriately discharged through the rotary damper 6a. On the other hand, fresh water W (or slaked lime slurry) having a predetermined pressure is supplied into the inner pipe 15 of the spraying device 7 through the spray water amount control valve 10b, and the spraying air A 0 having a predetermined pressure is supplied to the spraying air supply port 14a. Air control valve 19
Supplied through. As a result, a predetermined amount of spray particles are ejected into the gas temperature reduction tower 5, mixed with the exhaust gas H and evaporated to cool the exhaust gas H.
【0018】噴霧粒子との混合により冷却された低温排
ガスHaは、ガス減温塔5の上方部から排ガス導出ダク
ト2を経て集塵装置3へ導入され、清浄化される。減温
された排ガスHaの温度は、ガス減温塔5の出口側に設
けた温度検出器10aによって検出されており、当該温
度検出器10aの検出信号により噴霧水量制御弁10b
の開度が制御され、これによって排ガスHaの温度が制
御される。また、減温された排ガスHaの流量がガス減
温塔5の出口側に於いてガス流量測定装置11によって
検出され、その検出信号がガス熱量演算装置12へ入力
される。前記ガス熱量演算装置12へは温度検出制御装
置9からの排ガス温度信号が入力されており、排ガス熱
量(ガス流量×ガス温度×ガス比熱)が演算されると共
に、その演算信号が噴霧装置7の噴霧角度の調整駆動装
置9へ入力される。The low-temperature exhaust gas Ha cooled by mixing with the spray particles is introduced into the dust collector 3 from the upper part of the gas temperature reducing tower 5 through the exhaust gas discharge duct 2 and is cleaned. The temperature of the cooled exhaust gas Ha is detected by a temperature detector 10a provided on the outlet side of the gas cooling tower 5, and the spray water amount control valve 10b is detected by the detection signal of the temperature detector 10a.
Of the exhaust gas Ha is controlled, which controls the temperature of the exhaust gas Ha. The flow rate of the exhaust gas Ha whose temperature has been reduced is detected by the gas flow rate measuring device 11 at the outlet side of the gas temperature reducing tower 5, and the detection signal is input to the gas calorie calculation device 12. The exhaust gas temperature signal from the temperature detection control device 9 is input to the gas heat amount calculation device 12, and the exhaust gas heat amount (gas flow rate × gas temperature × gas specific heat) is calculated, and the calculation signal is supplied to the spray device 7. It is input to the drive unit 9 for adjusting the spray angle.
【0019】前記角度調整駆動装置9は、演算制御装置
11からの排ガス熱量信号が大であれば噴霧装置7から
の噴霧水の噴出角度αが大(広角噴霧)となるように、
また逆に排ガス熱量が小の場合には噴出角度αが小(狭
角噴霧)となるように、前記内管移動用レバー18aを
移動させる。即ち、本実施例に於いては、前記調整駆動
装置9は内管移動用レバー18aに一端を軸支したラッ
ク9cと、当該ラック9cと噛合するギヤ9bと、ギヤ
9bの回転用のモータ9aとから構成されており、モー
タ9aの回転によりレバー18aが所定の方向へ移動さ
れると、前述の通りねじ機構を介して内管15が移動さ
れ、その先端に固定したノズルフレア16と外管14の
先端に固定したノズルキャップ13との間の間隙が拡大
(又は縮少)して、噴霧水の噴出角度αが広角(又は狭
角)となる。The angle adjusting drive device 9 is arranged so that, if the exhaust gas heat quantity signal from the arithmetic and control unit 11 is large, the spray angle α of the spray water from the spray device 7 is large (wide-angle spray).
On the contrary, when the exhaust gas heat amount is small, the inner pipe moving lever 18a is moved so that the ejection angle α becomes small (narrow-angle spray). That is, in the present embodiment, the adjustment drive device 9 includes the rack 9c whose one end is axially supported by the inner pipe moving lever 18a, the gear 9b meshing with the rack 9c, and the motor 9a for rotating the gear 9b. When the lever 18a is moved in a predetermined direction by the rotation of the motor 9a, the inner pipe 15 is moved through the screw mechanism as described above, and the nozzle flare 16 and the outer pipe fixed to the tip thereof are formed. The gap between the nozzle cap 13 fixed to the tip of the nozzle 14 and the nozzle cap 13 increases (or decreases), and the spray angle α of the sprayed water becomes a wide angle (or a narrow angle).
【0020】尚、本実施例では噴霧装置7やその噴霧角
度の調整駆動装置9を上述の如き構成としているが、噴
霧粒子の噴出角度αが調整可能であれば如何なる構造の
ものであってもよい。また、本実施例では噴霧装置7か
らの清水を噴霧するようにしているが、清水に替えて消
石灰スラリーを噴霧することも勿論可能である。In the present embodiment, the spraying device 7 and the spraying angle adjusting drive device 9 are configured as described above, but any structure may be used as long as the spraying angle α of the sprayed particles can be adjusted. Good. Further, in this embodiment, fresh water from the spraying device 7 is sprayed, but it is of course possible to spray slaked lime slurry instead of fresh water.
【0021】[0021]
【発明の効果】本件発明では、ガス減温塔5内へ水は消
石灰スラリーを噴霧するための噴霧装置7を噴霧粒子の
噴出角度αが調整自在な構造とすると共に、排ガス熱量
が大で大量の減温水等の噴霧を必要とする場合には噴出
角度αを大に、また逆に、排ガス熱量が小で比較的小量
の減温水等を噴霧する際には噴出角度αを小に調整する
構成としている。その結果、噴霧する減温水量が多い場
合でも、噴霧パターン内の噴霧粒子密度が減少して排ガ
スとの接触効率が高まり、噴霧粒子は短時間内にガスと
混合して完全蒸発をすることになり、ガス減温塔5の高
さ寸法の引き下げが可能となる。また、噴霧する減温水
量が小量の場合には、噴出角度αを狭角とすることによ
り噴霧粒子の完全蒸発までの水平方向移動距離が減少
し、ガス減温塔の塔径の縮小が可能となる。本発明は上
述の通り、排ガス減温装置4の大幅な小形化と、噴霧水
滴が直接衝突することに起因する塔壁腐食を完全に防止
することができ、優れた実用的効用を奏するものであ
る。According to the present invention, the spray device 7 for spraying slaked lime slurry into water into the gas temperature reduction tower 5 has a structure in which the spray angle α of spray particles can be adjusted, and the heat quantity of exhaust gas is large and large. If the spraying of reduced temperature water, etc. is required, the jetting angle α is adjusted to a large value. It is configured to do. As a result, even if the amount of dehumidified water to be sprayed is large, the density of spray particles in the spray pattern is reduced and the contact efficiency with the exhaust gas is increased, and the spray particles mix with the gas within a short time to complete evaporation. Therefore, the height of the gas temperature reducing tower 5 can be reduced. In addition, when the amount of dehumidifying water to be sprayed is small, by making the ejection angle α a narrow angle, the horizontal movement distance until complete evaporation of the spray particles is reduced, and the tower diameter of the gas desuperheater is reduced. It will be possible. INDUSTRIAL APPLICABILITY As described above, the present invention is capable of completely reducing the size of the exhaust gas temperature reducing device 4 and completely preventing the corrosion of the tower wall caused by the direct collision of the sprayed water droplets, and has an excellent practical effect. is there.
【図1】本発明に係る排ガス減温装置の系統概要図であ
る。FIG. 1 is a schematic diagram of a system of an exhaust gas temperature reducing device according to the present invention.
【図2】本発明で使用する噴霧装置の縦断面図である。FIG. 2 is a vertical sectional view of a spraying device used in the present invention.
【図3】広角噴霧状態にある噴霧装置のノズル部の拡大
図である。FIG. 3 is an enlarged view of a nozzle portion of the spraying device in a wide-angle spraying state.
【図4】狭角噴霧状態にある噴霧装置のノズル部の拡大
図である。FIG. 4 is an enlarged view of a nozzle portion of the spraying device in a narrow-angle spraying state.
【図5】噴霧パターンが一定である従前の噴霧装置に於
いて、ガス量が減少した場合の噴霧パターンの一例を示
すものである。FIG. 5 shows an example of a spray pattern when the amount of gas is reduced in a conventional spray device having a constant spray pattern.
【図6】噴霧パターンが一定である従前の噴霧装置に於
いて、ガス量が増加した場合の噴霧パターンの一例を示
すものである。FIG. 6 shows an example of a spray pattern when the amount of gas is increased in a conventional spray device having a constant spray pattern.
【図7】狭角噴霧パターンの一例を示す説明図である。FIG. 7 is an explanatory diagram showing an example of a narrow-angle spray pattern.
【図8】広角噴霧パターンの一例を示す説明図である。FIG. 8 is an explanatory diagram showing an example of a wide-angle spray pattern.
【図9】ガス量が大となる場合の噴霧粒子の運動の一例
を示す説明図である。FIG. 9 is an explanatory diagram showing an example of the movement of spray particles when the amount of gas is large.
【図10】ガス量が小となる場合の噴霧粒子の運動の一
例を示す説明図である。FIG. 10 is an explanatory diagram showing an example of movement of spray particles when the amount of gas is small.
H 高温排ガス W 噴霧水 A0 噴霧用空気 Ha 低温排ガス α 噴出角度 1 排ガス導入ダクト 2 排ガス導出ダクト 3 集塵装置 4 排ガス減温装置 5 ガス減温塔 5a 整流板 6 ダストセパレータ 6a ロータリダンパ 7 噴霧装置 8 噴霧パターン制御装置 9 噴出角度の調整駆動装置 9a モータ 9b ギヤ 9c ラック 10 ガス温度制御装置 10a 温度検出器 10b 噴霧水量制御弁 11 ガス流量測定装置 12 ガス熱量演算装置 13 ノズルキャップ 14 外管 14a 噴霧水供給孔 15 内管 15a 空気孔 16 ノズルフレア 17 噴霧水噴出口 18 内管移動機構 18a 内管移動用レバー 18b ねじ 19 空気制御弁H High-temperature exhaust gas W Spray water A 0 Spraying air Ha Low-temperature exhaust gas α Jet angle 1 Exhaust gas introduction duct 2 Exhaust gas discharge duct 3 Dust collector 4 Exhaust gas temperature reducing device 5 Gas temperature reducing tower 5a Rectifier plate 6 Dust separator 6a Rotary damper 7 Spraying Device 8 Spray pattern control device 9 Jet angle adjustment drive device 9a Motor 9b Gear 9c Rack 10 Gas temperature control device 10a Temperature detector 10b Spray water amount control valve 11 Gas flow rate measurement device 12 Gas calorie calculation device 13 Nozzle cap 14 Outer tube 14a Spray water supply hole 15 Inner tube 15a Air hole 16 Nozzle flare 17 Spray water jet 18 Inner tube moving mechanism 18a Inner tube moving lever 18b Screw 19 Air control valve
Claims (3)
(5)と;ガス減温塔(5)内へ水又は消石灰スラリー
を噴霧すると共に、その噴出角度(α)を調整自在とし
た噴霧装置(7)と;減温排ガス温度を検出し、その検
出信号により消石灰スラリーの噴霧量を調節する排ガス
温度制御装置(10)と;排ガスの熱量が増えると前記
噴出角度(α)を大にし、また排ガスの熱量が減ると噴
出角度(α)を小にする噴霧パターン制御装置(8)と
より構成した排ガス減温装置。1. A vertical gas temperature reduction tower (5) through which exhaust gas flows; water or slaked lime slurry is sprayed into the gas temperature reduction tower (5), and its ejection angle (α) is adjustable. A spraying device (7); an exhaust gas temperature control device (10) for detecting a reduced temperature exhaust gas temperature and adjusting the spray amount of the slaked lime slurry based on the detection signal; and increasing the jet angle (α) as the exhaust gas heat amount increases. In addition, the exhaust gas temperature control device comprising a spray pattern control device (8) that reduces the ejection angle (α) when the heat amount of the exhaust gas decreases.
測定装置(11)及びガス温度検出器(10a)と、ガ
ス流量及びガス温度の検出値から排ガスの熱量を演算す
るガス熱量演算装置(12)と、前記演算装置(12)
からの信号により噴出角度(α)を調整する駆動装置
(9)とより構成した請求項1に記載の排ガス減温装
置。2. A spray pattern control device (8), a gas flow rate measuring device (11) and a gas temperature detector (10a), and a gas calorific value computing device for computing the calorific value of exhaust gas from detected values of the gas flow rate and gas temperature ( 12) and the arithmetic unit (12)
The exhaust gas temperature reducing device according to claim 1, further comprising a drive device (9) for adjusting an ejection angle (α) according to a signal from the exhaust gas temperature reducing device.
噴霧装置(7)により水又は消石灰スラリーを噴霧して
排ガスを減温する排ガス減温方法に於いて、排ガス流量
と排ガス温度を検出し、前記排ガス温度の検出値により
噴霧水又は消石灰スラリーの噴霧量を調整して排ガス温
度を制御すると共に、前記排ガス流量と排ガス温度の検
出値から排ガス熱量を演算し、排ガス熱量の演算値が増
えると前記噴霧装置(7)からの噴霧粒子の噴出角度
(α)を増す方向に、また排ガス熱量が減少すると前記
噴出角度(α)を減す方向に夫々制御することを特徴と
する排ガス減温方法。3. An exhaust gas temperature reducing method for spraying water or slaked lime slurry by a spraying device (7) into a gas temperature reducing tower (5) through which exhaust gas flows to cool the exhaust gas, and the exhaust gas flow rate and the exhaust gas temperature. To control the exhaust gas temperature by adjusting the spray amount of spray water or slaked lime slurry according to the detected value of the exhaust gas temperature, calculate the exhaust gas heat amount from the exhaust gas flow rate and the detected value of the exhaust gas temperature, the exhaust gas heat amount calculation When the value is increased, the spraying angle (α) of the sprayed particles from the spraying device (7) is increased, and when the exhaust gas heat amount is decreased, the spraying angle (α) is decreased. Exhaust gas temperature reduction method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3255856A JP2587738B2 (en) | 1991-09-06 | 1991-09-06 | Exhaust gas cooling device and exhaust gas cooling method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3255856A JP2587738B2 (en) | 1991-09-06 | 1991-09-06 | Exhaust gas cooling device and exhaust gas cooling method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0566009A true JPH0566009A (en) | 1993-03-19 |
| JP2587738B2 JP2587738B2 (en) | 1997-03-05 |
Family
ID=17284542
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3255856A Expired - Fee Related JP2587738B2 (en) | 1991-09-06 | 1991-09-06 | Exhaust gas cooling device and exhaust gas cooling method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2587738B2 (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0798109A (en) * | 1993-09-30 | 1995-04-11 | Mitsumine Kogyo Kk | Incinerator and combustion gas treatment |
| JP2002219323A (en) * | 2001-01-30 | 2002-08-06 | Ishikawajima Harima Heavy Ind Co Ltd | Gas cooling tower |
| JP2002364831A (en) * | 2001-06-08 | 2002-12-18 | Takuma Co Ltd | Exhaust gas cooling method and its device |
| CN113041808A (en) * | 2021-03-23 | 2021-06-29 | 光大环保技术装备(常州)有限公司 | Method and system for controlling adding amount of lime slurry and cooling water in deacidification tower |
| CN116947144A (en) * | 2023-09-21 | 2023-10-27 | 山东中禹环境工程有限公司 | Flue gas evaporation wastewater treatment system |
-
1991
- 1991-09-06 JP JP3255856A patent/JP2587738B2/en not_active Expired - Fee Related
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0798109A (en) * | 1993-09-30 | 1995-04-11 | Mitsumine Kogyo Kk | Incinerator and combustion gas treatment |
| JP2002219323A (en) * | 2001-01-30 | 2002-08-06 | Ishikawajima Harima Heavy Ind Co Ltd | Gas cooling tower |
| JP2002364831A (en) * | 2001-06-08 | 2002-12-18 | Takuma Co Ltd | Exhaust gas cooling method and its device |
| CN113041808A (en) * | 2021-03-23 | 2021-06-29 | 光大环保技术装备(常州)有限公司 | Method and system for controlling adding amount of lime slurry and cooling water in deacidification tower |
| CN116947144A (en) * | 2023-09-21 | 2023-10-27 | 山东中禹环境工程有限公司 | Flue gas evaporation wastewater treatment system |
| CN116947144B (en) * | 2023-09-21 | 2023-12-08 | 山东中禹环境工程有限公司 | Flue gas evaporation wastewater treatment system |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2587738B2 (en) | 1997-03-05 |
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