JPH04277005A - Exhaust gas treatment apparatus of urban garbage incinerator - Google Patents
Exhaust gas treatment apparatus of urban garbage incineratorInfo
- Publication number
- JPH04277005A JPH04277005A JP3059614A JP5961491A JPH04277005A JP H04277005 A JPH04277005 A JP H04277005A JP 3059614 A JP3059614 A JP 3059614A JP 5961491 A JP5961491 A JP 5961491A JP H04277005 A JPH04277005 A JP H04277005A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- activated carbon
- adsorption tower
- tower
- gas treatment
- 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
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 116
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 43
- 239000004071 soot Substances 0.000 claims abstract description 21
- 239000000126 substance Substances 0.000 claims abstract description 19
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 17
- 238000001179 sorption measurement Methods 0.000 claims description 45
- 239000000428 dust Substances 0.000 claims description 20
- 239000002245 particle Substances 0.000 claims description 18
- 238000003795 desorption Methods 0.000 claims description 14
- 239000002699 waste material Substances 0.000 claims description 14
- 239000012717 electrostatic precipitator Substances 0.000 claims description 9
- 238000002156 mixing Methods 0.000 claims description 2
- 230000001172 regenerating effect Effects 0.000 claims 1
- 239000007789 gas Substances 0.000 abstract description 65
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 abstract description 9
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 9
- 229910000041 hydrogen chloride Inorganic materials 0.000 abstract description 8
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 abstract description 8
- 238000000034 method Methods 0.000 abstract description 4
- 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 abstract 1
- 239000012716 precipitator Substances 0.000 abstract 1
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 21
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 8
- 150000002013 dioxins Chemical class 0.000 description 7
- 238000010586 diagram Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 229910052815 sulfur oxide Inorganic materials 0.000 description 5
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 4
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 4
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 description 3
- 238000002347 injection Methods 0.000 description 3
- 239000007924 injection Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000012159 carrier gas Substances 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 238000010612 desalination reaction Methods 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
- 230000023556 desulfurization Effects 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 229910000040 hydrogen fluoride Inorganic materials 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 241000790917 Dioxys <bee> Species 0.000 description 1
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 description 1
- 229910003556 H2 SO4 Inorganic materials 0.000 description 1
- 229910017917 NH4 Cl Inorganic materials 0.000 description 1
- 229910017900 NH4 F Inorganic materials 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 229910052731 fluorine Inorganic materials 0.000 description 1
- 239000011737 fluorine Substances 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000010977 unit operation Methods 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Electrostatic Separation (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は、特に都市ゴミ焼却炉の
排ガスから排出された煤じん、塩素、フッ素、窒素酸化
物、イオウ酸化物、ダイオキシン、重金属等の有害物質
を同時処理できる都市ゴミ焼却炉の排ガス処理装置に関
する。[Industrial Application Field] The present invention is particularly useful for municipal waste that can simultaneously process harmful substances such as soot, chlorine, fluorine, nitrogen oxides, sulfur oxides, dioxins, and heavy metals discharged from the exhaust gas of municipal waste incinerators. This invention relates to an incinerator exhaust gas treatment device.
【0002】0002
【従来の技術】都市ゴミ焼却炉から排出される排ガスに
は、下記表1に示すように、煤じんを初めとして、塩化
水素(HCl )、窒素酸化物(NOx )、イオウ酸
化物(SOx )、ダイオキシン等の化学物質、重金属
等の固体や気体の有害物質が含まれているため、これら
有害物質を排ガスから除去することが周辺環境、地球環
境を保全する上で極めて重要である。[Prior Art] As shown in Table 1 below, the exhaust gas emitted from municipal waste incinerators contains soot, hydrogen chloride (HCl), nitrogen oxides (NOx), and sulfur oxides (SOx). , chemical substances such as dioxins, and solid and gaseous harmful substances such as heavy metals, it is extremely important to remove these harmful substances from exhaust gas in order to preserve the surrounding environment and the global environment.
【0003】0003
【表1】[Table 1]
【0004】従来、上記有害物質の除去対策は、煤じん
を除去する集じん、NOx を除去する脱硝、SOx
を除去する脱硫、塩化水素を除去する脱塩等の各単位操
作を、例えば直列に接続した排ガス処理設備を用いて、
排ガスを段階的に、しかも有害物質を個別に処理する方
法で行われている。[0004] Conventionally, measures to remove the above-mentioned harmful substances include dust collection to remove soot, denitrification to remove NOx, and SOx.
Each unit operation, such as desulfurization to remove hydrogen chloride and desalination to remove hydrogen chloride, can be carried out using, for example, exhaust gas treatment equipment connected in series.
This is done by treating exhaust gas in stages and treating harmful substances individually.
【0005】[0005]
【発明が解決しようとする課題】しかしながら、有害物
質を個別に且つ段階的に処理する上記排ガス処理設備は
、大きな設置スペースを必要とするため設備費がかかり
過ぎる欠点がある。However, the above-mentioned exhaust gas treatment equipment that treats harmful substances individually and in stages has the disadvantage that it requires a large installation space and is therefore expensive.
【0006】又、上記従来の処理設備では、ダイオキシ
ンや重金属を除去することが技術的に対応できていない
ため、これらを除去するためには新たな設備を更に追加
しなければならず、それ故に一段と大きな設置スペース
が必要になるという問題もある。[0006] Furthermore, since the conventional treatment equipment described above is not technically capable of removing dioxins and heavy metals, it is necessary to add new equipment to remove them. There is also the problem that a larger installation space is required.
【0007】本発明は、前記従来の問題点を解決するべ
くなされたもので、煤じん、塩化水素、NOx 、SO
x 、ダイオキシン、重金属等の有害物質を実質上同時
処理により除去することができ、それ故に設備スペース
を小さくすることができる都市ゴミ焼却炉排ガス処理装
置を提供することを課題とする。[0007] The present invention was made to solve the above-mentioned conventional problems, and it
It is an object of the present invention to provide a municipal waste incinerator exhaust gas treatment device that can remove harmful substances such as x, dioxins, heavy metals, etc. by substantially simultaneous treatment, and can therefore reduce the equipment space.
【0008】[0008]
【課題を解決するための手段】本発明は、都市ゴミ焼却
炉の排ガスから有害物質を除去する都市ゴミ焼却炉の排
ガス処理装置において、排ガスから煤じんを除去する電
気集じん装置と、排ガスにアンモニアを注入・混合する
手段と、煤じん除去後の排ガスをアンモニアと共に通過
させ、該排ガス中の有害物質を吸着して除去する、活性
炭が充填された吸着塔と、吸着塔内の活性炭を、排ガス
の通過方向と略直交する方向に移動させ、該吸着塔外へ
切出す手段と、切出した活性炭を再生させる脱離塔と、
再生した活性炭を前記吸着塔内に戻す手段とを備えるこ
とにより、前記課題を解決したものである。[Means for Solving the Problems] The present invention provides an electrostatic precipitator for removing soot and dust from the exhaust gas, and an electrostatic precipitator for removing soot and dust from the exhaust gas, in an exhaust gas treatment device for a municipal garbage incinerator that removes harmful substances from the exhaust gas of the municipal garbage incinerator. A means for injecting and mixing ammonia, an adsorption tower filled with activated carbon that allows exhaust gas after soot and dust removal to pass together with ammonia, and adsorbs and removes harmful substances in the exhaust gas, and activated carbon in the adsorption tower. means for moving the activated carbon in a direction substantially perpendicular to the passing direction of the exhaust gas and cutting it out of the adsorption tower; a desorption tower that regenerates the cut activated carbon;
The above problem has been solved by providing means for returning the regenerated activated carbon into the adsorption tower.
【0009】本発明は、又、上記都市ゴミ焼却炉排ガス
処理装置において、吸着塔が、排ガスの通過方向に沿っ
て複数の充填室に仕切られ、これら充填室には、排ガス
の入口に近いものから順に粒径の大きな活性炭が充填さ
れており、且つ、各充填室の活性炭を、排ガスの通過方
向と略直交する方向に移動させ、各充填室外へ切出す段
と、切出した活性炭を脱離塔で再生した後、粒径毎に分
級する手段と、分級した活性炭を粒径に応じた前記各充
填室に戻す手段とが設置された構成にすることにより、
一層確実に前記課題を解決したものである。The present invention also provides the above-mentioned municipal waste incinerator exhaust gas treatment device, in which the adsorption tower is partitioned into a plurality of filling chambers along the exhaust gas passage direction, and these filling chambers include one near the exhaust gas inlet. Activated carbon of larger particle size is filled in order from 1 to 3, and the activated carbon in each filling chamber is moved in a direction substantially perpendicular to the exhaust gas passage direction to cut it out of each filling chamber, and the cut activated carbon is desorbed. After being regenerated in the tower, the structure is equipped with a means for classifying the activated carbon according to particle size and a means for returning the classified activated carbon to each of the filling chambers according to the particle size.
This more reliably solves the above problem.
【0010】0010
【作用】一般に都市ガスには煤じんが多く含まれている
が、本発明においては、排ガスをまず電気集じん装置で
処理するようにしている。その結果、大部分の煤じんは
この段階で除去される。[Operation] Generally, city gas contains a lot of soot and dust, but in the present invention, the exhaust gas is first treated with an electrostatic precipitator. As a result, most of the soot and dust is removed at this stage.
【0011】次いで、除去しきれなかった煤じんと他の
有害物質を含有する排ガスを、アンモニアと共に吸着塔
を通過させると、排ガスが吸着塔を通過する際に、該排
ガス中に含まれる塩化水素(HCl )、フッ化水素(
HF)、二酸化イオウ(SO2)は、混合されたアンモ
ニアとそれぞれ次の(1)〜(3)式に示した反応をす
るため、これら有害物質はその反応生成物として容易に
活性炭に吸着させて除去できる。なお、式中(A)は「
吸着」を表わしている。Next, when the exhaust gas containing soot and other harmful substances that could not be completely removed is passed through an adsorption tower together with ammonia, hydrogen chloride contained in the exhaust gas is removed as it passes through the adsorption tower. (HCl), hydrogen fluoride (
HF) and sulfur dioxide (SO2) react with mixed ammonia as shown in the following equations (1) to (3), so these harmful substances can be easily adsorbed onto activated carbon as reaction products. Can be removed. In addition, (A) in the formula is “
It represents "adsorption".
【0012】
(1) HCl + NH3 → NH4
Cl (A)(2) HF + NH3 →
NH4 F(A)(3) SO2 +1/2O2
+NH3 +H2 O→ NH4 (H)SO4
(A)
SO2 +1/2O2 +H2 O
→ H2 SO4 (A)(1) HCl + NH3 → NH4
Cl (A) (2) HF + NH3 →
NH4 F(A)(3) SO2 +1/2O2
+NH3 +H2 O→ NH4 (H)SO4
(A) SO2 +1/2O2 +H2 O → H2 SO4 (A)
【0013】又、排ガス中に含まれているNOx は、
活性炭が触媒となり、次の(4)、(5)式に示すよう
に、アンモニアにより無害な窒素に還元できるため確実
に除去できる。[0013] Furthermore, NOx contained in the exhaust gas is
Activated carbon acts as a catalyst, and as shown in the following equations (4) and (5), it can be reduced to harmless nitrogen by ammonia, so it can be removed reliably.
【0014】
(4) NO+NH3 +1/4O2
→ N2 +3/2H2 O (
5) NO2 +4/3NH3 → 7/6N
2 +2H2 O(4) NO+NH3 +1/4O2
→ N2 +3/2H2 O (
5) NO2 +4/3NH3 → 7/6N
2 +2H2 O
【0015】更に、排ガス中に含まれ
ているダイオキシンや重金属は、活性炭に吸着されるた
め除去できる。Furthermore, dioxins and heavy metals contained in the exhaust gas can be removed because they are adsorbed by the activated carbon.
【0016】本発明においては、又、吸着塔に充填され
ている活性炭が、排ガスの通過方向に略直交する方向に
移動し、該吸着塔外へ切出されるので、排ガスとの接触
時間が長く、吸着能が低下した活性炭から順次系外へ取
出すことができる。そして、切出した活性炭を脱離塔で
再生し、吸着塔に戻すようにしているため、吸着能が回
復した活性炭を吸着塔内へ順次補充することができる。In the present invention, the activated carbon packed in the adsorption tower moves in a direction substantially perpendicular to the direction in which the exhaust gas passes and is cut out of the adsorption tower, so the contact time with the exhaust gas is extended. , activated carbon whose adsorption capacity has decreased can be sequentially removed from the system. Since the cut activated carbon is regenerated in the desorption tower and returned to the adsorption tower, the activated carbon whose adsorption capacity has been recovered can be sequentially replenished into the adsorption tower.
【0017】又、吸着塔を、排ガスの通過方向に沿って
複数の充填室に仕切り、排ガスの入口に近い充填室程粒
径の大きな(粒子の粗い)活性炭を充填し、排ガスの出
口に近い充填室程粒径の小さな活性炭を充填するように
したので、煤じんの除去効率が大幅に向上され、又排ガ
スの通過が阻害されることも防止できるので、排ガス処
理効果も向上する。In addition, the adsorption tower is divided into a plurality of packed chambers along the exhaust gas passage direction, and the closer the packed chamber is to the exhaust gas inlet, the larger the particle size (coarse particles) of activated carbon is filled, and the closer to the exhaust gas outlet is filled with activated carbon. Since the activated carbon having a smaller particle size is filled in the filling chamber, the removal efficiency of soot and dust is greatly improved, and since the passage of exhaust gas can be prevented from being obstructed, the exhaust gas treatment effect is also improved.
【0018】従って、本発明によれば、排ガス中に含ま
れる前記有害物質を実質上同時処理の短工程処理により
除去するため、設備スペースを大幅に縮小することがで
きる。Therefore, according to the present invention, since the harmful substances contained in the exhaust gas are removed by substantially simultaneous short-step processing, the equipment space can be significantly reduced.
【0019】又、排ガスを処理しながら、吸着能が低下
した活性炭を再生することができるため、排ガス処理装
置を連続運転することもできる。Furthermore, since the activated carbon whose adsorption capacity has decreased can be regenerated while treating the exhaust gas, the exhaust gas treatment apparatus can be operated continuously.
【0020】又、脱離塔は、不活性ガス雰囲気で加熱脱
離操作を行う場合、比較的低温(例えば、300〜40
0℃)でダイオキシ等を分解することができる。[0020] Furthermore, when performing a thermal desorption operation in an inert gas atmosphere, the desorption tower is used at a relatively low temperature (for example, 300 to 40
Dioxy, etc. can be decomposed at 0℃).
【0021】[0021]
【実施例】以下、図面を参照して、本発明の実施例を詳
細に説明する。Embodiments Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings.
【0022】図1は、本発明の第1実施例の都市ゴミ焼
却炉の排ガス処理装置を示す概略構成図である。FIG. 1 is a schematic diagram showing an exhaust gas treatment device for a municipal waste incinerator according to a first embodiment of the present invention.
【0023】本実施例は、図示しない都市ゴミ焼却炉か
らの排ガスを最初に処理する電気集じん装置10と、該
集じん装置で処理した排ガスに、アンモニアを注入・混
合するアンモニア注入手段12と、アンモニアが混合さ
れた排ガスを通過させて処理する吸着塔14と、該吸着
塔14から切出した活性炭を再生処理する脱離塔16と
を備えている。This embodiment includes an electrostatic precipitator 10 that initially processes exhaust gas from a municipal garbage incinerator (not shown), and an ammonia injection means 12 that injects and mixes ammonia into the exhaust gas treated by the dust collector. , an adsorption tower 14 that passes through and processes exhaust gas mixed with ammonia, and a desorption tower 16 that regenerates the activated carbon cut out from the adsorption tower 14.
【0024】上記電気集じん装置10は、都市ゴミの排
ガス中に多く含まれる煤じんを重点的に除去するもので
、集められた煤じんは、下端のロールフィーダ18a
から取出し可能になっている。[0024] The electrostatic precipitator 10 is designed to intensively remove soot and dust contained in large amounts in the exhaust gas of municipal waste, and the collected soot and dust are transferred to the roll feeder 18a at the lower end.
It can be taken out from.
【0025】上記吸着塔12は、入口ルーバ、活性炭層
、出口ルーバ(図示せず)で構成され、粒径4〜10m
mの粒状の活性炭が充填されている。アンモニアが混合
された排ガスは、該吸着塔12を図中右方向に通過し、
活性炭による吸着処理を受けた後、右上部に取付けられ
ている配管を介して煙突へ排出されるようになっている
。The adsorption tower 12 is composed of an inlet louver, an activated carbon layer, and an outlet louver (not shown), and has a particle size of 4 to 10 m.
Filled with m granular activated carbon. The exhaust gas mixed with ammonia passes through the adsorption tower 12 in the right direction in the figure,
After being adsorbed with activated carbon, it is discharged into the chimney via a pipe attached to the upper right corner.
【0026】又、上記吸着塔14では、充填されている
活性炭が下方(排ガスの通過方向に直交する方向)に移
動し、排ガスとの接触時間が長いものから順次下端のロ
ールフィーダ18b により外へ切出されるようになっ
ている。In addition, in the adsorption tower 14, the charged activated carbon moves downward (in a direction perpendicular to the direction in which the exhaust gas passes), and the activated carbon that has been in contact with the exhaust gas for a longer time is sequentially transported to the outside by the roll feeder 18b at the lower end. It is designed to be cut out.
【0027】吸着塔14の外へ切出された吸着能が低下
した活性炭は、移送コンベア20aで前記脱離塔16の
上部へ供給される。The activated carbon cut out of the adsorption tower 14 and having a reduced adsorption capacity is supplied to the upper part of the desorption tower 16 by a transfer conveyor 20a.
【0028】上記脱離塔16では、不活性なキャリアガ
スが導入されて、該キャリアガスの存在下で活性炭は間
接加熱される。加熱温度としては、例えば300〜65
0℃の範囲で適切な温度を選択することができる。In the desorption column 16, an inert carrier gas is introduced, and the activated carbon is indirectly heated in the presence of the carrier gas. The heating temperature is, for example, 300 to 65
An appropriate temperature can be selected within the range of 0°C.
【0029】上記間接加熱の結果、活性炭から脱離した
不要ガスは、オフガス処理装置22へ導入され、所定の
処理を受ける。一方、不要なガスが脱離したために吸着
能を回復した再生活性炭は、脱離塔16の下端のロール
フィーダ18cよりスクリーン24に切出される。[0029] As a result of the above indirect heating, the unnecessary gas desorbed from the activated carbon is introduced into the off-gas treatment device 22 and undergoes a predetermined treatment. On the other hand, the regenerated activated carbon whose adsorption capacity has been recovered due to the removal of unnecessary gas is cut out to the screen 24 from the roll feeder 18c at the lower end of the desorption tower 16.
【0030】上記スクリーン24に切出された再生活性
炭は、該スクリーン24により粉じんと分離され、移送
コンベア20b により搬送され、前記吸着塔14の上
部に供給される。The recycled activated carbon cut into the screen 24 is separated from dust by the screen 24, conveyed by the transfer conveyor 20b, and supplied to the upper part of the adsorption tower 14.
【0031】本実施例では、以上の動作が連続的に繰り
返されている。In this embodiment, the above operations are continuously repeated.
【0032】次に、本実施例の作用を説明する。Next, the operation of this embodiment will be explained.
【0033】都市ゴミ焼却炉からの排ガスは、まず電気
集じん装置10に導入され、大部分の煤じんはこの装置
で除去される。The exhaust gas from the municipal waste incinerator is first introduced into the electrostatic precipitator 10, and most of the soot and dust is removed by this device.
【0034】除去しきれなかった煤じんと排ガスとは、
アンモニア注入手段12から注入されたアンモニアと共
に、次の吸着塔14に導入される。[0034] The soot and dust and exhaust gas that could not be completely removed are:
Together with the ammonia injected from the ammonia injection means 12, it is introduced into the next adsorption tower 14.
【0035】煤じんは充填されている活性炭により完全
に捉えられ、且つ塩化水素、フッ化水素、イオウ酸化物
は、アンモニアの存在下で前述した(1)〜(3)式に
示した反応をして活性炭に容易に吸着され、窒素酸化物
は前記(4)、(5)式に従い、無害な物質に変化させ
られ、更に、ダイオキシンや重金属も活性炭に吸着され
る。[0035] Soot and dust are completely captured by the packed activated carbon, and hydrogen chloride, hydrogen fluoride, and sulfur oxide undergo the reactions shown in equations (1) to (3) above in the presence of ammonia. Nitrogen oxides are easily adsorbed on activated carbon, and nitrogen oxides are converted into harmless substances according to the above equations (4) and (5). Furthermore, dioxins and heavy metals are also adsorbed on activated carbon.
【0036】このように、上記吸着塔14では、煤じん
、塩化水素、フッ化水素、イオウ酸化物、窒素酸化物、
更には従来対策が難しかったダイオキシン、重金属等の
全てを、同時処理により除去することが可能となる。In this manner, the adsorption tower 14 collects soot, dust, hydrogen chloride, hydrogen fluoride, sulfur oxides, nitrogen oxides,
Furthermore, it becomes possible to remove all of dioxins, heavy metals, etc., which were difficult to deal with in the past, by simultaneous treatment.
【0037】又、上記有害物質を吸着した活性炭は、そ
の吸着量の多いものから順に吸着塔14の下部から切出
され、脱離塔16で再生され、再び吸着塔14の上部に
供給される。従って、常時、都市ゴミ焼却炉の排ガス処
理装置を、十分な吸着能の下で連続運転することも可能
である。[0037] Furthermore, the activated carbon that has adsorbed the harmful substances is cut out from the lower part of the adsorption tower 14 in descending order of adsorption amount, is regenerated in the desorption tower 16, and is again supplied to the upper part of the adsorption tower 14. . Therefore, it is also possible to constantly operate the exhaust gas treatment device of the municipal waste incinerator under sufficient adsorption capacity.
【0038】本実施例の都市ゴミ焼却炉の排ガス処理装
置を、排ガス処理に実際に適用したところ、下記表2に
示した結果が得られた。When the exhaust gas treatment device for a municipal waste incinerator of this example was actually applied to exhaust gas treatment, the results shown in Table 2 below were obtained.
【0039】[0039]
【表2】[Table 2]
【0040】上記表2より、本実施例は、極めて優れた
排ガスの浄化処理能力を有していることが明らかである
。From Table 2 above, it is clear that this example has an extremely excellent exhaust gas purification ability.
【0041】なお、本実施例では、図2に示すように、
電気集じん装置10と吸着塔14とを直結し、アンモニ
アを吸着塔14の入り口ルーバ25の手前に注入するよ
うにしてもよい。In this embodiment, as shown in FIG.
The electrostatic precipitator 10 and the adsorption tower 14 may be directly connected, and ammonia may be injected into the adsorption tower 14 in front of the entrance louver 25.
【0042】図3は、第2実施例に係る都市ゴミ焼却炉
の排ガス処理装置の要部である吸着塔を示す概略構成図
である。FIG. 3 is a schematic diagram showing an adsorption tower which is a main part of an exhaust gas treatment device for a municipal waste incinerator according to a second embodiment.
【0043】本実施例の都市ゴミ焼却炉の排ガス処理装
置は、吸着塔を除き、他の基本構成は前記第1実施例と
実質的に同一である。The exhaust gas treatment system for a municipal waste incinerator according to this embodiment has substantially the same basic structure as the first embodiment except for the adsorption tower.
【0044】本実施例では、吸着塔14が、排ガスの通
過方向に沿って第1、第2及び第3充填室14a 、1
4b 及び14c に仕切られている。各充填室の境界
は、気体は通過できるが活性炭は通過できないようにな
っている。In this embodiment, the adsorption tower 14 has first, second and third filled chambers 14a, 1 along the exhaust gas passage direction.
It is divided into 4b and 14c. The boundaries of each filling chamber are designed to allow gas to pass through but not activated carbon.
【0045】そして、第1充填室14a には粒径15
〜10mmの粗い活性炭が、第2充填室14b には粒
径10〜6mmの中程度の活性炭が、第3充填室14c
には粒径4〜3mmの細い活性炭がそれぞれ充填され
るようになっている。[0045] The first filling chamber 14a contains particles with a particle size of 15
Coarse activated carbon with a particle size of ~10 mm is placed in the second filling chamber 14b, medium activated carbon with a particle size of 10 to 6 mm is placed in the third filling chamber 14c.
are each filled with thin activated carbon having a particle size of 4 to 3 mm.
【0046】又、各充填室14a 、14b 、14c
の下部には活性炭を切出すロールフィーダ18d 、
18e 、18f が設けられ、切出された活性炭は一
括して脱離塔へ移送され、再生処理がなされるようにな
っている。[0046] Also, each filling chamber 14a, 14b, 14c
At the bottom of the roll feeder 18d for cutting activated carbon,
18e and 18f are provided, and the cut activated carbon is transferred all at once to a desorption tower, where it is regenerated.
【0047】脱離塔で再生された活性炭は、篩分機26
でそれぞれ所定の粒径に分級され、再び対応する各充填
室14a 、14b 、14c に戻されるようになっ
ている。[0047] The activated carbon regenerated in the desorption tower is passed through the sieve machine 26.
The particles are classified into predetermined particle sizes and returned to the corresponding filling chambers 14a, 14b, and 14c.
【0048】本実施例によれば、煤じんによる吸着塔1
4の目詰りを防止できるため、前記第1実施例と同様の
効果が一段と発揮される上に、該煤じんを効率良く除去
することもできる。According to this embodiment, the adsorption tower 1 due to soot and dust
4 can be prevented from clogging, the same effects as those of the first embodiment can be further exhibited, and the soot and dust can also be efficiently removed.
【0049】以上、本発明について具体的に説明したが
、本発明は前記実施例に示したものに限定されるもので
ないことはいうまでもない。Although the present invention has been specifically explained above, it goes without saying that the present invention is not limited to what has been shown in the above embodiments.
【0050】例えば、吸着塔を複数の充填室に仕切る場
合、2つ又は4つ以上であってもよい。For example, when the adsorption tower is partitioned into a plurality of packed chambers, the number may be two or four or more.
【0051】なお、本発明の処理装置は都市ゴミ焼却炉
の排ガスに限らず、一般の排ガス処理にも利用すること
もできる。The treatment apparatus of the present invention can be used not only for treating exhaust gas from municipal waste incinerators, but also for general exhaust gas treatment.
【0052】[0052]
【発明の効果】以上説明した通り、本発明によれば、都
市ゴミ焼却炉の排ガスに対して、集じん、脱塩、脱硝、
脱硫、ダイオキシン除去、重金属除去を同時に実行でき
るので、排ガス処理設備を簡略化することができ、スペ
ース効率を大幅に向上できるという優れた効果が得られ
る。[Effects of the Invention] As explained above, according to the present invention, dust collection, desalination, denitrification, and
Since desulfurization, dioxin removal, and heavy metal removal can be performed simultaneously, the exhaust gas treatment equipment can be simplified and space efficiency can be greatly improved, which is an excellent effect.
【0053】又、排ガスの通過方向に沿って吸着塔を複
数の充填室に仕切り、ガス入口に近い充填室程活性炭の
粒径を大きくする場合には、排ガスの処理効率を一段と
向上できるという優れた効果が得られる。[0053] Furthermore, if the adsorption tower is divided into a plurality of packed chambers along the exhaust gas passage direction, and the particle size of the activated carbon is made larger in the packed chambers closer to the gas inlet, there is an advantage that the exhaust gas treatment efficiency can be further improved. You can get the same effect.
【図1】図1は、第1実施例の都市ゴミ焼却炉排ガス処
理装置を示す概略構成図である。FIG. 1 is a schematic configuration diagram showing a municipal garbage incinerator exhaust gas treatment device according to a first embodiment.
【図2】図2は、第1実施例の変形例の要部を示す概略
構成図である。FIG. 2 is a schematic configuration diagram showing main parts of a modification of the first embodiment.
【図3】図3は、第2実施例の要部を示す概略構成図で
ある。FIG. 3 is a schematic configuration diagram showing main parts of a second embodiment.
10…電気集じん装置、
12…アンモニア注入手段、
14…吸着塔、
14a 〜14c …充填室、
16…脱離塔、
18a 〜18f …ロールフィーダ、20a 、20
b …移送コンベア、
26…篩分機。DESCRIPTION OF SYMBOLS 10... Electrostatic precipitator, 12... Ammonia injection means, 14... Adsorption tower, 14a-14c... Filling chamber, 16... Desorption tower, 18a-18f... Roll feeder, 20a, 20
b...Transfer conveyor, 26...Sieving machine.
Claims (2)
去する都市ゴミ焼却炉の排ガス処理装置において、排ガ
スから煤じんを除去する電気集じん装置と、排ガスにア
ンモニアを注入・混合する手段と、煤じん除去後の排ガ
スをアンモニアと共に通過させ、該排ガス中の有害物質
を吸着して除去する、活性炭が充填された吸着塔と、吸
着塔内の活性炭を、排ガスの通過方向と略直交する方向
に移動させ、該吸着塔外へ切出す手段と、切出した活性
炭を再生させる脱離塔と、再生した活性炭を前記吸着塔
内に戻す手段と、を備えていることを特徴とする都市ゴ
ミ焼却炉の排ガス処理装置。Claim 1: An exhaust gas treatment device for a municipal garbage incinerator that removes harmful substances from the exhaust gas of a municipal garbage incinerator, comprising an electrostatic precipitator that removes soot and dust from the exhaust gas, and a means for injecting and mixing ammonia into the exhaust gas. , an adsorption tower filled with activated carbon that passes through the exhaust gas after soot and dust removal together with ammonia and adsorbs and removes harmful substances in the exhaust gas; and the activated carbon in the adsorption tower is arranged approximately perpendicular to the direction of passage of the exhaust gas. Municipal garbage, comprising means for moving the activated carbon in the direction and cutting it out of the adsorption tower, a desorption tower for regenerating the cut activated carbon, and a means for returning the regenerated activated carbon into the adsorption tower. Incinerator exhaust gas treatment equipment.
過方向に沿って複数の充填室に仕切られ、これら充填室
には、排ガスの入口に近いものから順に粒径の大きな活
性炭が充填されており、且つ、各充填室の活性炭を、排
ガスの通過方向と略直交する方向に移動させ、各充填室
外へ切出す段と、切出した活性炭を脱離塔で再生した後
、粒径毎に分級する手段と、分級した活性炭を粒径に応
じた前記各充填室に戻す手段と、が設置されていること
を特徴とする都市ゴミ焼却炉の排ガス処理装置。2. In claim 1, the adsorption tower is partitioned into a plurality of packed chambers along the exhaust gas passage direction, and these packed chambers are filled with activated carbon having a larger particle size in order from the one closest to the exhaust gas inlet. In addition, the activated carbon in each filling chamber is moved in a direction substantially perpendicular to the exhaust gas passage direction and cut out of each filling chamber, and after the cut activated carbon is regenerated in a desorption tower, it is separated by particle size. 1. An exhaust gas treatment device for a municipal waste incinerator, comprising means for classifying the activated carbon into particles, and means for returning the classified activated carbon to each of the filling chambers according to the particle size.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5961491A JPH0779943B2 (en) | 1991-03-01 | 1991-03-01 | Exhaust gas treatment equipment for municipal waste incinerators |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5961491A JPH0779943B2 (en) | 1991-03-01 | 1991-03-01 | Exhaust gas treatment equipment for municipal waste incinerators |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04277005A true JPH04277005A (en) | 1992-10-02 |
| JPH0779943B2 JPH0779943B2 (en) | 1995-08-30 |
Family
ID=13118302
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP5961491A Expired - Fee Related JPH0779943B2 (en) | 1991-03-01 | 1991-03-01 | Exhaust gas treatment equipment for municipal waste incinerators |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0779943B2 (en) |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH04300628A (en) * | 1991-03-29 | 1992-10-23 | Kubota Corp | Dry treatment method for waste incineration gas |
| JPH06210138A (en) * | 1992-11-26 | 1994-08-02 | Nippon Steel Corp | Dry exhaust gas purification treatment method, blast furnace operating method, and sintering machine operating method |
| EP0901801A1 (en) * | 1997-09-10 | 1999-03-17 | Sumitomo Heavy Industries, Ltd. | Process for low temperature pyrolysis of dioxins |
| JP2007083221A (en) * | 2005-08-24 | 2007-04-05 | Jfe Steel Kk | Exhaust gas treatment method |
| JP2007083222A (en) * | 2005-08-25 | 2007-04-05 | Jfe Steel Kk | Exhaust gas treatment method |
| JP2007090320A (en) * | 2005-09-05 | 2007-04-12 | Jfe Steel Kk | Exhaust gas treatment equipment |
| JP2008531244A (en) * | 2005-02-08 | 2008-08-14 | グロコウスキー、ホルスト | Method for purifying exhaust gas produced by a sintering process of ores and / or other metal-containing substances in metal production |
| JP2010512984A (en) * | 2006-12-14 | 2010-04-30 | グロコウスキー、ホルスト | Method and apparatus for purifying exhaust gas in the sintering process of ores and / or other metal-containing materials in metal production |
| JP2010167377A (en) * | 2009-01-23 | 2010-08-05 | Chubu Electric Power Co Inc | Gas treatment system |
| CN112275129A (en) * | 2020-09-04 | 2021-01-29 | 山西太钢工程技术有限公司 | Flue gas emission treatment method and equipment |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6454089A (en) * | 1987-05-07 | 1989-03-01 | Fuller H B Co | Thermally stable reactive hot melt urethane adhesive composition containing thermoplastic polymer, cured urethane polyalkylene polyol prepolymer having adaptability and sticking imparting agent |
-
1991
- 1991-03-01 JP JP5961491A patent/JPH0779943B2/en not_active Expired - Fee Related
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6454089A (en) * | 1987-05-07 | 1989-03-01 | Fuller H B Co | Thermally stable reactive hot melt urethane adhesive composition containing thermoplastic polymer, cured urethane polyalkylene polyol prepolymer having adaptability and sticking imparting agent |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH04300628A (en) * | 1991-03-29 | 1992-10-23 | Kubota Corp | Dry treatment method for waste incineration gas |
| JPH06210138A (en) * | 1992-11-26 | 1994-08-02 | Nippon Steel Corp | Dry exhaust gas purification treatment method, blast furnace operating method, and sintering machine operating method |
| EP0901801A1 (en) * | 1997-09-10 | 1999-03-17 | Sumitomo Heavy Industries, Ltd. | Process for low temperature pyrolysis of dioxins |
| JP2008531244A (en) * | 2005-02-08 | 2008-08-14 | グロコウスキー、ホルスト | Method for purifying exhaust gas produced by a sintering process of ores and / or other metal-containing substances in metal production |
| JP2007083221A (en) * | 2005-08-24 | 2007-04-05 | Jfe Steel Kk | Exhaust gas treatment method |
| JP2007083222A (en) * | 2005-08-25 | 2007-04-05 | Jfe Steel Kk | Exhaust gas treatment method |
| JP2007090320A (en) * | 2005-09-05 | 2007-04-12 | Jfe Steel Kk | Exhaust gas treatment equipment |
| JP2010512984A (en) * | 2006-12-14 | 2010-04-30 | グロコウスキー、ホルスト | Method and apparatus for purifying exhaust gas in the sintering process of ores and / or other metal-containing materials in metal production |
| JP2010167377A (en) * | 2009-01-23 | 2010-08-05 | Chubu Electric Power Co Inc | Gas treatment system |
| CN112275129A (en) * | 2020-09-04 | 2021-01-29 | 山西太钢工程技术有限公司 | Flue gas emission treatment method and equipment |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0779943B2 (en) | 1995-08-30 |
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