JPS6238738Y2 - - Google Patents
Info
- Publication number
- JPS6238738Y2 JPS6238738Y2 JP16455083U JP16455083U JPS6238738Y2 JP S6238738 Y2 JPS6238738 Y2 JP S6238738Y2 JP 16455083 U JP16455083 U JP 16455083U JP 16455083 U JP16455083 U JP 16455083U JP S6238738 Y2 JPS6238738 Y2 JP S6238738Y2
- Authority
- JP
- Japan
- Prior art keywords
- hydrogen chloride
- equipment
- hcl
- exhaust gas
- absorption liquid
- 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.)
- Expired
Links
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 63
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims description 62
- 229910000041 hydrogen chloride Inorganic materials 0.000 claims description 62
- 239000007789 gas Substances 0.000 claims description 47
- 239000002250 absorbent Substances 0.000 claims description 32
- 230000002745 absorbent Effects 0.000 claims description 32
- 238000002347 injection Methods 0.000 claims description 20
- 239000007924 injection Substances 0.000 claims description 20
- 239000007788 liquid Substances 0.000 claims description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 17
- 238000001816 cooling Methods 0.000 claims description 16
- 239000000428 dust Substances 0.000 claims description 11
- 238000010521 absorption reaction Methods 0.000 claims description 10
- 239000000725 suspension Substances 0.000 claims description 8
- 238000010790 dilution Methods 0.000 claims description 7
- 239000012895 dilution Substances 0.000 claims description 7
- 239000007795 chemical reaction product Substances 0.000 claims description 6
- 238000004090 dissolution Methods 0.000 claims description 5
- 230000001105 regulatory effect Effects 0.000 claims description 4
- 238000007865 diluting Methods 0.000 claims description 2
- 238000000034 method Methods 0.000 description 12
- 239000011575 calcium Substances 0.000 description 11
- 239000000498 cooling water Substances 0.000 description 8
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 6
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 5
- 229910052791 calcium Inorganic materials 0.000 description 5
- 239000011734 sodium Substances 0.000 description 5
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- 229910052708 sodium Inorganic materials 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 239000000292 calcium oxide Substances 0.000 description 3
- 235000012255 calcium oxide Nutrition 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 239000012530 fluid Substances 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 239000000779 smoke Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 1
- 239000006096 absorbing agent Substances 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 150000004045 organic chlorine compounds Chemical class 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- -1 polyvinyl chloride Chemical class 0.000 description 1
- 239000004800 polyvinyl chloride Substances 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000012716 precipitator Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000009257 reactivity Effects 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Chimneys And Flues (AREA)
Description
【考案の詳細な説明】
本考案は、焼却炉排ガスに含まれる塩化水素
(HCl)を効率よく除去する装置に関するもので
ある。[Detailed Description of the Invention] The present invention relates to an apparatus that efficiently removes hydrogen chloride (HCl) contained in incinerator exhaust gas.
焼却炉、とくに産業廃棄物及び家庭廃棄物を対
象とする焼却炉の排ガスには、ポリ塩化ビニルに
代表される有機塩素系化合物に由来するHClが高
濃度に含まれており、2次公害防止のためにこれ
らを除去する設備が必要である。 The exhaust gas from incinerators, especially incinerators for industrial and household waste, contains high concentrations of HCl derived from organic chlorine compounds such as polyvinyl chloride, and it is important to prevent secondary pollution. Therefore, equipment to remove these is necessary.
排ガスのHClを除去するには、一般にアルカリ
性HCl吸収剤が用いられるが、その方法として
は、大別として、乾式、湿式、半湿式の3つの除
去方法がある。 An alkaline HCl absorbent is generally used to remove HCl from exhaust gas, and there are three main methods for removing HCl: dry, wet, and semi-wet.
乾式除去方法は、粉状のHCl吸収剤を排ガス中
に噴霧してHClと気固反応させ、その反応生成物
を粉体として回収するものである。HCl吸収剤と
しては、安価なカルシウム系の石灰石
(CaCO3)、消石灰(Ca(OH)2)、生石灰
(CaO)が多用される。これは気固反応であるか
ら、噴霧する吸収剤の粒径、表面状態が反応に大
きく影響し、一般にHClに対する吹込み当量比を
大きくしないと除去率が悪く、ごみ焼却炉の場合
にはCa(OH)2でHClを430ppm以下に規制するた
めには、通常流入HCl当り3当量以上の吹込みを
要し、また粉体は液体にくらべて注入量制御がむ
ずかしく、過剰注入に設定制御せざるをえなかつ
た。 In the dry removal method, a powdered HCl absorbent is sprayed into exhaust gas to cause a gas-solid reaction with HCl, and the reaction product is recovered as a powder. As HCl absorbents, inexpensive calcium-based limestone (CaCO 3 ), slaked lime (Ca(OH) 2 ), and quicklime (CaO) are often used. Since this is a gas-solid reaction, the particle size and surface condition of the sprayed absorbent greatly affect the reaction.In general, the removal rate is poor unless the injection equivalent ratio to HCl is increased, and in the case of a garbage incinerator, Ca In order to control HCl to 430ppm or less with (OH) 2 , it is usually necessary to inject 3 equivalents or more per inflowing HCl, and it is difficult to control the injection amount for powders compared to liquids, so it is difficult to control the injection amount by setting excessive injection. I had no choice but to colander.
また、湿式除去方法は、HCl吸収剤を溶解また
は懸濁させたHCl吸収液で排ガスを洗浄するもの
である。この方法では、一般にナトリウム系吸収
剤が多用されるが、溶解度の小さいカルシウム系
吸収剤は懸濁液として使用することになり、ガス
洗浄塔や洗浄液循環系統に懸濁した吸収剤が堆積
したり付着固定したりするので、装置の維持管理
が困難である。しかしナトリウム系吸収剤を使用
する場合でも、単価が高いのでランニングコスト
が割高になり、さらに洗浄液接液部にスケールが
析出する等のトラブルも生じる。また、洗浄液
は、吸収剤の追加と液の一部更新をしなければな
らないので、排液処理が必要となり、さらに、洗
浄された排ガスは通常数十度まで過冷却されるの
で、煙突より大気放散させる前に白煙防止のため
に再加熱しなければならず、前記の乾式除去方法
にくらべて、装置のイニシヤルコストも格段に高
いものになる。 In addition, the wet removal method cleans the exhaust gas with an HCl absorbing liquid in which an HCl absorbent is dissolved or suspended. In this method, sodium-based absorbents are generally used extensively, but calcium-based absorbents with low solubility are used as a suspension, which prevents the suspended absorbent from accumulating in the gas scrubbing tower or cleaning fluid circulation system. Maintenance of the device is difficult because it is stuck and fixed. However, even when a sodium-based absorbent is used, the unit price is high, resulting in relatively high running costs, and problems such as scale precipitation on areas in contact with the cleaning liquid occur. In addition, the cleaning fluid requires addition of absorbent and partial renewal of the fluid, which necessitates drainage treatment.Furthermore, the cleaned exhaust gas is usually supercooled to several tens of degrees, so it passes through the chimney into the atmosphere. It must be reheated to prevent white smoke before being dissipated, and the initial cost of the equipment is much higher than in the dry removal method described above.
また、第3のHCl除去方法として、HCl吸収剤
を溶解又は懸濁させた液を排ガス中に噴霧して、
液滴を排ガスの熱により蒸発乾固し、粉体として
回収する方法、いわゆる半湿式除去方法がある。
この方法は、湿式法のように多くの付帯設備(排
水処理、白煙防止など)を必要とせずに乾式法よ
りも効率よくHClを除去できる利点があるが、
HCl除去率の向上、吹込み当量比の低減のために
は、吸収剤を可能な限り低濃度にし、微細な水滴
として排ガス中に噴霧する必要がある。しかしな
がら、低濃度で噴霧するためには膨大な溶解懸濁
設備と供給設備が必要になる。また、安価なCa
(OH)2を吸収剤として使用する場合、水への溶解
度が小さい(Ca(OH)2で約1.7Kg/m3)ために、
懸濁液として噴霧せざるをえないが、懸濁粒子が
HClと反応する前に水滴が蒸発乾固すると、Ca
(OH)2粒子の表面の細孔が閉塞してしまうので、
反応性は逆に悪化する。 In addition, as a third HCl removal method, a liquid in which an HCl absorbent is dissolved or suspended is sprayed into the exhaust gas.
There is a so-called semi-wet removal method in which droplets are evaporated to dryness using the heat of exhaust gas and recovered as powder.
This method has the advantage of being able to remove HCl more efficiently than the dry method without requiring many incidental facilities (e.g., wastewater treatment, white smoke prevention, etc.) like the wet method.
In order to improve the HCl removal rate and reduce the injection equivalent ratio, it is necessary to reduce the concentration of the absorbent to the lowest possible level and spray it into the exhaust gas as fine water droplets. However, spraying at low concentrations requires extensive dissolution and suspension equipment and supply equipment. Also, cheap Ca
When (OH) 2 is used as an absorbent, due to its low solubility in water (approximately 1.7 Kg/m 3 for Ca(OH) 2 ),
It has to be sprayed as a suspension, but suspended particles
When water droplets evaporate to dryness before reacting with HCl, Ca
(OH) 2 Since the pores on the surface of the particles are blocked,
On the contrary, reactivity worsens.
本考案は、このような従来のHCl除去装置が抱
える欠点を解消し、焼却炉排ガスのHClを効率よ
く、操作性容易に除去できる装置を提供すること
を目的とするものである。 The present invention aims to eliminate the drawbacks of conventional HCl removal devices, and to provide a device that can efficiently remove HCl from incinerator exhaust gas with ease of operation.
本考案は、
焼却炉排ガスのガス冷却室に設けられた噴射
ノズルに給水するための供給ポンプ設備、
HCl吸収液をうるためのHCl吸収剤の溶解懸
濁設備、
前記HCl吸収液の供給ポンプ設備、
前記HCl吸収液を前記噴射ノズルに給水する
水により希釈するための希釈設備、
前記希釈されたHCl吸収液を前記噴射ノズル
に導く手段、
前記ガス冷却室から流出するHCl吸収剤と
HClの反応生成物を除去するための除塵設備、
とからなることを特徴とするものである。 The present invention includes: supply pump equipment for supplying water to an injection nozzle installed in a gas cooling chamber for incinerator exhaust gas; equipment for dissolving and suspending an HCl absorbent to obtain an HCl absorption liquid; and supply pump equipment for the HCl absorption liquid. , dilution equipment for diluting the HCl absorbent with water supplied to the injection nozzle, means for guiding the diluted HCl absorbent to the injection nozzle, HCl absorbent flowing out from the gas cooling chamber;
Dust removal equipment for removing HCl reaction products.
さらに本発明の一実施例を図面を参照しながら
説明すると、Aは焼却炉であつて、発生する高温
排ガスが流過する煙道Bによつてガス冷却室Cに
連なつている。ガス冷却室Cには噴射ノズル1が
配備されており、ガス冷却室Cの出口には電気集
塵機、マルチサイクロンなどの除塵設備Dが設け
られ、この除塵設備Dはさらに誘引送風機2を介
して図示しない煙突に連なつている。 Further, one embodiment of the present invention will be described with reference to the drawings. A is an incinerator, which is connected to a gas cooling chamber C by a flue B through which generated high-temperature exhaust gas flows. The gas cooling chamber C is equipped with an injection nozzle 1, and the outlet of the gas cooling chamber C is equipped with dust removal equipment D such as an electric precipitator or a multi-cyclone. It is connected to a chimney.
Eはガス冷却水3の供給ポンプ設備で、たとえ
ば流量調整弁4を備え、またラインミキサなどの
希釈設備Fを介して前記噴射ノズル1のヘツダ管
5に連なつている。また、GはHCl吸収剤6と水
7とを混合してHCl吸収液8をうるための溶解懸
濁設備であつて、HCl吸収液8の流量調整弁9を
備えた供給ポンプ設備Hを介して前記希釈設備F
に連なつている。 Reference numeral E denotes a supply pump equipment for the gas cooling water 3, which is equipped with, for example, a flow rate regulating valve 4, and is connected to the header pipe 5 of the injection nozzle 1 via a dilution equipment F such as a line mixer. Further, G is a dissolving/suspending equipment for mixing the HCl absorbent 6 and water 7 to obtain an HCl absorbing liquid 8, and G is a dissolving and suspending equipment for mixing the HCl absorbing agent 6 and water 7 to obtain an HCl absorbing liquid 8. The dilution equipment F
It is connected to.
しかして、焼却炉Aで発生したHClを含む高温
排ガスは煙道Bを経て、ガス冷却室Cで供給ポン
プ設備Eによりガス冷却水3が噴射ノズル1から
噴射され、所定温度まで冷却されるが、排ガス中
のHClを除去するためのHCl吸収剤6は溶解懸濁
設備Gにおいて水7が加えられて溶液状又は懸濁
状のHCl吸収液8となつて貯留される。このHCl
吸収剤6としては、NaOH、Na2CO3などのナト
リウム系アルカリ成分、Ca(OH)2、CaOなどの
カルシウム系アルカリ成分が使用され、濃度が5
〜20%になるように水7を加える。なお、カルシ
ウム系の成分は水に対する溶解度が小さいので、
懸濁状態で貯留するために常時撹拌する必要があ
る。 The high temperature exhaust gas containing HCl generated in the incinerator A passes through the flue B and is cooled to a predetermined temperature by the supply pump equipment E injecting gas cooling water 3 from the injection nozzle 1 in the gas cooling chamber C. Water 7 is added to the HCl absorbent 6 for removing HCl in the exhaust gas in the dissolution/suspension equipment G, and the HCl absorbent 8 is stored as a solution or suspension. This HCl
As the absorbent 6, sodium-based alkaline components such as NaOH and Na 2 CO 3 and calcium-based alkaline components such as Ca(OH) 2 and CaO are used, and the concentration is 5.
Add 7 parts water to ~20%. Note that calcium-based components have low solubility in water, so
Constant stirring is required to store it in a suspended state.
前記溶解懸濁設備GにおけるHCl吸収液8は、
供給ポンプ設備H及び流量調整弁9を経て希釈設
備Fでガス冷却室Cで噴射されるガス冷却水3と
混合されてさらに希薄となり、ヘツダ管5を経由
して噴射ノズル1からガス冷却室C内に噴射さ
れ、HClとHCl吸収剤とは反応するとともに液滴
は排ガスの熱により蒸発固化し、その反応生成物
は粉体となつて流出するガス流に伴われて除塵設
備Dで捕集される。また、ガス冷却室C内粗大粒
子はガス冷却室Cの下部から取り出され、場合に
よつては再びHCl吸収剤6として再使用される。 The HCl absorption liquid 8 in the dissolution and suspension equipment G is:
It is mixed with the gas cooling water 3 injected in the gas cooling chamber C at the dilution facility F through the supply pump equipment H and the flow rate adjustment valve 9 to become further diluted, and then flows from the injection nozzle 1 to the gas cooling chamber C via the header pipe 5. The HCl and HCl absorbent react with each other, and the droplets evaporate and solidify due to the heat of the exhaust gas.The reaction product becomes powder and is collected by dust removal equipment D along with the outflowing gas flow. be done. Further, coarse particles in the gas cooling chamber C are taken out from the lower part of the gas cooling chamber C, and are reused as the HCl absorbent 6 as the case may be.
なお、除塵設備Dの入口温度が一定値(250〜
350℃)になるようにガス冷却水3の供給量を制
御すべく、除塵設備Dの入口温度と流量調整弁4
又はポンプとを自動制御回路10により関連さ
せ、また排ガス中のHCl濃度、たとえば除塵設備
D出口又は煙道BにおけるHCl濃度を計測して、
それを設定値又は規制値まで除去するに足る化学
当量比のHCl吸収液8を流量調整弁9又はポンプ
で流量制御する自動制御回路11を設けると便利
である。 Note that the inlet temperature of dust removal equipment D is a constant value (250~
In order to control the supply amount of gas cooling water 3 so that the temperature is 350℃), the inlet temperature and flow rate adjustment valve 4 of dust removal equipment D are
or by associating the pump with the automatic control circuit 10 and measuring the HCl concentration in the exhaust gas, for example, the HCl concentration at the exit of the dust removal equipment D or the flue B,
It is convenient to provide an automatic control circuit 11 that controls the flow rate of the HCl absorbing liquid 8 with a chemical equivalence ratio sufficient to remove it to a set value or regulation value using a flow rate regulating valve 9 or a pump.
また、HCl吸収液8の供給量を排ガス中のHCl
濃度の変動に追従させるためには、希釈設備Fか
ら噴射ノズル1までの液保持時間が最短となるよ
うにガス冷却水3とHCl吸収液8の混合点を考慮
する必要があり、HCl吸収液8の供給量をガス冷
却水3の供給量から減算処理する制御系統を設け
ると除塵設備D入口の温度調節をより正確に行な
うことができる。 In addition, the supply amount of HCl absorption liquid 8 is determined by the amount of HCl in the exhaust gas.
In order to follow the concentration fluctuations, it is necessary to consider the mixing point of the gas cooling water 3 and the HCl absorbing liquid 8 so that the liquid retention time from the dilution equipment F to the injection nozzle 1 is the shortest. By providing a control system that subtracts the supply amount of gas cooling water 3 from the supply amount of gas cooling water 3, the temperature at the inlet of the dust removal equipment D can be controlled more accurately.
以上述べたように、本考案によれば次のような
顕著な効果がえられるものである。 高温排ガ
スの減温のための噴射水量をすべてHCl吸収剤
の溶解懸濁のために利用できるから、吸収液濃
度を最大限に希釈することができる。そのため
に、ナトリウム系吸収剤はもちろん、溶解度の
低いカルシウム系吸収剤でもHCl除去率対HCl
吹込み当量比を従来の半湿式法にくらべて低減
でき、しかも従来の半湿式法のもつ利点(簡単
な設備、易操作性、反応生成物の捕集が容易)
を損うことがない。 As described above, according to the present invention, the following remarkable effects can be obtained. Since the amount of water injected for cooling the high-temperature exhaust gas can all be used for dissolving and suspending the HCl absorbent, the absorbent concentration can be diluted to the maximum. For this reason, not only sodium-based absorbents but also calcium-based absorbents with low solubility have a high HCl removal rate.
The blowing equivalent ratio can be reduced compared to the conventional semi-wet method, and the advantages of the conventional semi-wet method (simple equipment, easy operation, easy collection of reaction products)
There is no harm to it.
HCl吸収剤を最大限に希釈することができる
から、噴射ノズルの閉塞、配管やノズル先端部
へのスケール生成や反応生成物の付着などのト
ラブルが解消できる。 Since the HCl absorbent can be diluted to the maximum extent possible, problems such as blockage of the injection nozzle, scale formation on piping and nozzle tips, and adhesion of reaction products can be eliminated.
既設の水噴射式ガス冷却装置を有する焼却炉
にも容易に適用できる。 It can also be easily applied to incinerators with existing water injection gas cooling devices.
図面は本考案の一実施例を示す配置図である。
A……焼却炉、B……煙道、C……ガス冷却
室、D……除塵設備、E,H……供給ポンプ設
備、F……希釈設備、G……溶解懸濁設備、1…
…噴射ノズル、2……誘引送風機、3……ガス冷
却水、4,9……弁、5……ヘツダ管、6……
HCl吸収剤、7……水、8……HCl吸収液。
The drawing is a layout diagram showing an embodiment of the present invention. A... Incinerator, B... Flue, C... Gas cooling room, D... Dust removal equipment, E, H... Supply pump equipment, F... Dilution equipment, G... Dissolution suspension equipment, 1...
...Injection nozzle, 2...Induced blower, 3...Gas cooling water, 4, 9...Valve, 5...Header pipe, 6...
HCl absorbent, 7...water, 8...HCl absorbent.
Claims (1)
ノズルに給水するための供給ポンプ設備、塩化
水素吸収液をうるための塩化水素吸収剤の溶解
懸濁設備、前記塩化水素吸収液の供給ポンプ設
備、前記塩化水素吸収液を前記噴射ノズルに給
水する水により希釈するための希釈設備、前記
希釈された塩化水素吸収液を前記噴射ノズルに
導く手段、前記ガス冷却室から流出する塩化水
素吸収剤と塩化水素の反応生成物を除去するた
めの除塵設備とからなることを特徴とする焼却
炉排ガスの塩化水素除去装置。 2 前記噴射ノズルに給水するための供給ポンプ
設備が、流量調整弁を備えたものであつて、該
弁又はポンプによる水量が前記除塵設備入口温
度により制御されるものである実用新案登録請
求の範囲第1項記載の焼却炉排ガスの塩化水素
除去装置。 3 前記塩化水素吸収液の供給ポンプ設備が、流
量調整弁を備えたものであつて、該弁又はポン
プによる吸収液の流量が前記ガス冷却室入口又
は前記除塵設備出口における塩化水素濃度によ
り制御されるものである実用新案登録請求の範
囲第1項又は第2項記載の焼却炉排ガスの塩化
水素除去装置。[Claims for Utility Model Registration] 1. Supply pump equipment for supplying water to the injection nozzle provided in the gas cooling chamber for incinerator exhaust gas, hydrogen chloride absorbent dissolution and suspension equipment for obtaining hydrogen chloride absorption liquid, and the above-mentioned supply pump equipment for hydrogen chloride absorption liquid, dilution equipment for diluting the hydrogen chloride absorption liquid with water supplied to the injection nozzle, means for guiding the diluted hydrogen chloride absorption liquid to the injection nozzle, and the gas cooling chamber. 1. An apparatus for removing hydrogen chloride from incinerator exhaust gas, comprising a hydrogen chloride absorbent flowing out from the incinerator and dust removal equipment for removing reaction products of hydrogen chloride. 2. The scope of the utility model registration claim, wherein the supply pump equipment for supplying water to the injection nozzle is equipped with a flow rate regulating valve, and the amount of water by the valve or pump is controlled by the temperature at the inlet of the dust removal equipment. The hydrogen chloride removal device for incinerator exhaust gas according to item 1. 3. The supply pump equipment for the hydrogen chloride absorption liquid is equipped with a flow rate regulating valve, and the flow rate of the absorption liquid by the valve or pump is controlled by the hydrogen chloride concentration at the inlet of the gas cooling chamber or the outlet of the dust removal equipment. An apparatus for removing hydrogen chloride from incinerator exhaust gas according to claim 1 or 2 of the utility model registration claim.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16455083U JPS6083027U (en) | 1983-10-26 | 1983-10-26 | Hydrogen chloride removal equipment for incinerator exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16455083U JPS6083027U (en) | 1983-10-26 | 1983-10-26 | Hydrogen chloride removal equipment for incinerator exhaust gas |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS6083027U JPS6083027U (en) | 1985-06-08 |
JPS6238738Y2 true JPS6238738Y2 (en) | 1987-10-02 |
Family
ID=30360728
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP16455083U Granted JPS6083027U (en) | 1983-10-26 | 1983-10-26 | Hydrogen chloride removal equipment for incinerator exhaust gas |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS6083027U (en) |
-
1983
- 1983-10-26 JP JP16455083U patent/JPS6083027U/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS6083027U (en) | 1985-06-08 |
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