JPH0779943B2 - Exhaust gas treatment equipment for municipal waste incinerators - Google Patents
Exhaust gas treatment equipment for municipal waste incineratorsInfo
- Publication number
- JPH0779943B2 JPH0779943B2 JP5961491A JP5961491A JPH0779943B2 JP H0779943 B2 JPH0779943 B2 JP H0779943B2 JP 5961491 A JP5961491 A JP 5961491A JP 5961491 A JP5961491 A JP 5961491A JP H0779943 B2 JPH0779943 B2 JP H0779943B2
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- activated carbon
- adsorption tower
- soot
- 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.)
- Expired - Fee Related
Links
- 239000002699 waste material Substances 0.000 title claims description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 96
- 238000001179 sorption measurement Methods 0.000 claims description 45
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 39
- 239000000428 dust Substances 0.000 claims description 23
- 238000011049 filling Methods 0.000 claims description 22
- 239000004071 soot Substances 0.000 claims description 19
- 239000000126 substance Substances 0.000 claims description 17
- 229910021529 ammonia Inorganic materials 0.000 claims description 15
- 238000003795 desorption Methods 0.000 claims description 15
- 239000002245 particle Substances 0.000 claims description 13
- 238000002156 mixing Methods 0.000 claims description 3
- 230000001172 regenerating effect Effects 0.000 claims description 3
- 239000007789 gas Substances 0.000 description 61
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 23
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 8
- 229910001385 heavy metal Inorganic materials 0.000 description 8
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 7
- 229910052815 sulfur oxide Inorganic materials 0.000 description 7
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 6
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 6
- 238000010586 diagram Methods 0.000 description 5
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 4
- 150000002013 dioxins Chemical class 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 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
- 229910000040 hydrogen fluoride Inorganic materials 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
- 239000000460 chlorine Substances 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
- 230000023556 desulfurization Effects 0.000 description 2
- 239000012717 electrostatic precipitator Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- XLYOFNOQVPJJNP-ZSJDYOACSA-N heavy water Substances [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 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
- 239000011362 coarse particle Substances 0.000 description 1
- 238000005115 demineralization Methods 0.000 description 1
- 230000002328 demineralizing effect Effects 0.000 description 1
- 238000011033 desalting Methods 0.000 description 1
- 239000011737 fluorine Substances 0.000 description 1
- 229910052731 fluorine Inorganic materials 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method 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
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Electrostatic Separation (AREA)
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。FIELD OF THE INVENTION The present invention particularly relates to municipal waste capable of simultaneously treating harmful substances such as soot, chlorine, fluorine, nitrogen oxides, sulfur oxides, dioxins and heavy metals discharged from the exhaust gas of an urban refuse incinerator. The present invention relates to an exhaust gas treatment device for an incinerator.
【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。2. Description of the Related Art Exhaust gas emitted from an incinerator for municipal solid wastes contains, as shown in Table 1 below, soot, hydrogen chloride (HCl), nitrogen oxides (NOx) and sulfur oxides (SOx). Since it contains chemical substances such as dioxin, and solid or gaseous harmful substances such as heavy metals, it is extremely important to remove these harmful substances from the 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。Conventionally, the above-mentioned measures for removing harmful substances include unit operations such as dust collection for removing soot and dust, denitration for removing NOx, desulfurization for removing SOx, desalting for removing hydrogen chloride, for example, in series. It is performed by a method of treating exhaust gas stepwise and individually for harmful substances using connected exhaust gas treatment equipment.
【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 for treating harmful substances individually and stepwise has a drawback that the equipment cost is too high because it requires a large installation space.
【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。Further, in the above-mentioned conventional treatment equipment, since it is not technically possible to remove dioxin and heavy metals, new equipment must be added in order to remove them, therefore There is also a 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 、SOx
、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。The present invention has been made to solve the above-mentioned conventional problems. Soot, hydrogen chloride, NOx, SOx
It is an object of the present invention to provide an exhaust gas treatment device for an urban refuse incinerator, which can remove harmful substances such as dioxin, heavy metals and the like by substantially simultaneous treatment, and therefore can 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、前
記吸着塔が、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手段と、切出した活
性炭を前記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、前記課題を
解決したものである。DISCLOSURE OF THE INVENTION The present invention relates to an exhaust gas treatment apparatus for an urban refuse incinerator that removes harmful substances from the exhaust gas of an urban refuse incinerator, and an electric dust collector for removing soot and dust from the exhaust gas and an exhaust gas A means for injecting and mixing ammonia, an exhaust gas after soot removal is passed together with ammonia, and adsorbing and removing harmful substances in the exhaust gas, an adsorption tower filled with activated carbon, and an activated carbon in the adsorption tower, A means for moving the exhaust gas in a direction substantially orthogonal to the passing direction and cutting out the adsorption tower, and a desorption tower for regenerating the cut out activated carbon,
And means for returning the regenerated activated carbon to said adsorption tower, before
The adsorption tower is divided into a plurality of filling chambers along the passage direction of the exhaust gas, these filling chambers are filled with activated carbon having a large particle size in order from the one closer to the inlet of the exhaust gas, and
The activated carbon of each filling chamber is moved in the passing direction in a direction substantially perpendicular to the exhaust gas, and hand stage cut into each filling outdoor, after playing cut activated carbon in the desorption column, means for classifying the grain each diameter When, by means of returning the classified activated carbon in the respective filling chambers in accordance with the particle size is in the installed configuration, it is obtained by solving the previous SL problems.
【0009】[0009]
【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。In general, city gas contains a large amount of soot and dust, but in the present invention, the exhaust gas is first treated by the electric dust collector. As a result, most of the soot 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(H
F)、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。Then, the exhaust gas containing the soot dust and other harmful substances that cannot be completely removed is passed through the adsorption tower together with ammonia. When the exhaust gas passes through the adsorption tower, the hydrogen chloride contained in the exhaust gas is passed. (HC1), hydrogen fluoride (H
F) and sulfur dioxide (SO2) react with the mixed ammonia, respectively, as shown in the following formulas (1) to (3), so that these harmful substances are easily adsorbed on the activated carbon as their reaction products. Can be removed. In the formula (A), "adsorption" is represented.
【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。The NOx contained in the exhaust gas can be reliably removed because the activated carbon serves as a catalyst and can be reduced to harmless nitrogen by ammonia as shown in the following equations (4) and (5).
【0014】 (4) NO+NH3 +1/4O2 → N2 +3/2H2 O (5) NO2 +4/3NH3 → 7/6N2 +2H2 O(4) NO + NH3 + 1 / 4O2 → N2 + 3 / 2H2O (5) NO2 + 4 / 3NH3 → 7 / 6N2 + 2H2O
【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。Further, dioxins and heavy metals contained in the exhaust gas can be removed because they are adsorbed on 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 filled in the adsorption tower moves in a direction substantially orthogonal to the passage direction of the exhaust gas and is cut out of the adsorption tower, so that the contact time with the exhaust gas is long. It is possible to sequentially take out the activated carbon from the activated carbon having a reduced adsorption ability. Since the cut-off activated carbon is regenerated in the desorption tower and returned to the adsorption tower, the activated carbon whose adsorption capacity has been restored 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。Further, the adsorption tower is divided into a plurality of filling chambers along the passage direction of the exhaust gas, and the activated carbon having a larger particle size (coarse particles) is filled in the filling chamber closer to the exhaust gas inlet and closer to the exhaust gas outlet. Since the filling chamber is filled with activated carbon having a smaller particle size, the efficiency of removing soot and dust can be significantly improved, and the passage of exhaust gas can also be prevented, so that 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 the short-time treatment of substantially the same treatment, the equipment space can be greatly 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。Further, since the activated carbon having a reduced adsorption capacity can be regenerated while treating the exhaust gas, the exhaust gas treatment device can be continuously operated.
【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。Further, the desorption tower has a relatively low temperature (for example, 300 to 40) when the heat desorption operation is carried out in an inert gas atmosphere.
Dioxy and the like can be decomposed at 0 ° C.
【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 of the present invention will now be described in detail with reference to the drawings.
【0022】図1は、本発明の第1実施例の基本構成に
相当する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 shows the basic configuration of the first embodiment of the present invention.
It is a schematic block diagram which shows the exhaust gas processing apparatus of a corresponding municipal waste incinerator.
【0023】本基本構成は、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。The basic configuration of the present invention is an electrostatic precipitator 10 for initially treating exhaust gas from an unillustrated municipal refuse incinerator,
Ammonia is injected into the exhaust gas treated by the dust collector.
Ammonia injection means 12 for mixing, an adsorption tower 14 for treating the exhaust gas mixed with ammonia for treatment, and a desorption tower 16 for regenerating the activated carbon cut out from the adsorption tower 14.
It has and.
【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。The above-mentioned electric dust collector 10 focuses on removing soot and dust contained in the exhaust gas of municipal waste, and the collected soot and dust is the roll feeder 18a at the lower end.
It is possible to take 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3〜15
mm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 3 to 15
It is filled with mm granular activated carbon. The exhaust gas mixed with ammonia passes through the adsorption tower 12 in the right direction in the figure,
After receiving the adsorption treatment with activated carbon, it is discharged to the chimney through the pipe attached to the upper right part.
【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 activated carbon filled moves downward (in a direction orthogonal to the passage direction of the exhaust gas), and from the one having a long contact time with the exhaust gas 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。なお吸着塔14の具体的な構成は後
に詳述する。 The activated carbon, which is cut out of the adsorption tower 14 and has a reduced adsorption capacity, is supplied to the upper part of the desorption tower 16 by the transfer conveyor 20a. The specific structure of the adsorption tower 14 will be described later.
Will be described in detail.
【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 tower 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
A suitable temperature can be selected in 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。The unnecessary gas desorbed from the activated carbon as a result of the indirect heating is introduced into the off-gas treatment device 22 and subjected to a predetermined treatment. On the other hand, the regenerated activated carbon that has recovered its adsorption ability due to the desorption 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 regenerated activated carbon cut out on the screen 24 is separated into 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 operation is continuously repeated.
【0032】次に、説明の便宜上、先ずこの基本構成に
よって得られる作用から説明する。Next, for convenience of explanation, first, this basic structure will be described.
Therefore, the operation obtained will be described.
【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。Exhaust gas from the municipal refuse incinerator is first introduced into the electric dust collector 10 and most of the 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。The soot dust and exhaust gas that cannot be completely removed are
It is introduced into the next adsorption tower 14 together with the ammonia injected from the ammonia injection means 12.
【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。Soot and dust are completely caught by the activated carbon that has been filled, and hydrogen chloride, hydrogen fluoride and sulfur oxides undergo the reactions shown in the above formulas (1) to (3) in the presence of ammonia. Then, the nitrogen oxides are easily adsorbed on the activated carbon, the nitrogen oxides are converted into harmless substances according to the above formulas (4) and (5), and further, dioxins and heavy metals are also adsorbed on the 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。As described above, in the adsorption tower 14, all of soot dust, hydrogen chloride, hydrogen fluoride, sulfur oxides, nitrogen oxides, as well as dioxins, heavy metals and the like, which have been difficult to be dealt with in the past, are simultaneously removed. It becomes possible to do.
【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。The activated carbon having adsorbed the harmful substances is cut out from the lower part of the adsorption tower 14 in the order of the adsorbed amount, regenerated in the desorption tower 16 and supplied again to the upper part of the adsorption tower 14. . Therefore, it is possible to continuously operate the exhaust gas treatment device of the municipal refuse incinerator at a sufficient adsorption capacity.
【0038】本基本構成に係る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 treating apparatus for an urban refuse incinerator according to this basic structure 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、本基本構成は、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 basic configuration has an extremely excellent exhaust gas purification treatment capacity.
【0041】この基本構成は、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
変形してもよい。In this basic structure , as shown in FIG. 2, the electrostatic precipitator 10 and the adsorption tower 14 are directly connected to each other, and ammonia is injected in front of the inlet louver 25 of the adsorption tower 14.
It may be deformed .
【0042】図3は、前記基本構成における吸着塔14
の具体例を示す概略構成図である。FIG. 3 shows the adsorption tower 14 in the basic structure.
It is a schematic block diagram which shows the specific example of .
【0043】[0043]
【0044】この吸着塔14は、排ガスの通過方向に沿
って第1、第2及び第3充填室14a 、14b 及び14
c に仕切られている。各充填室14a 、14b 及び14
c 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。 The adsorption tower 14 has first, second and third filling chambers 14a, 14b and 14 along the passage direction of the exhaust gas.
Divided into c. Each filling chamber 14a, 14b and 14
At the boundary of c , gas can pass but activated carbon cannot pass.
【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。The particle size of the first filling chamber 14a is 15 to 15
Coarse activated carbon of 10 mm has a particle size of 10 in the second filling chamber 14b.
Medium activated carbon of ˜6 mm is filled in the third filling chamber 14c, and fine activated carbon having a particle size of 4 to 3 mm is filled in the third filling chamber 14c.
【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。Further, roll feeders 18d, 18e for cutting out the activated carbon are provided below the filling chambers 14a, 14b, 14c, respectively.
18f is provided, and the activated carbon that has been cut out is collectively transferred to the desorption tower for regeneration treatment.
【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。The activated carbon regenerated in the desorption tower is passed through the sieving machine 26.
The particles are classified to have a predetermined particle diameter and are returned to the corresponding filling chambers 14a, 14b and 14c again.
【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、前記基本構成と同様の効
果が一段と発揮される上に、該煤じんを更に効率良く除
去することができる。According to this embodiment, the adsorption tower 1 using soot and dust
Since the fourth clogging can be prevented, on the same effects as those of the basic configuration is further exerted, it is possible to further efficiently remove the soot dust.
【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 described above, it is needless to say that the present invention is not limited to those 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 packing chambers, the number of the adsorbing towers 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 is not limited to the exhaust gas of the municipal waste incinerator, but can be used 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。As described above, according to the present invention, dust collection, demineralization, denitration, and
Since desulfurization, dioxin removal, and heavy metal removal can be performed at the same time, the exhaust gas treatment equipment can be simplified and the space efficiency can be greatly improved, which is an excellent effect.
【0053】又、その際に、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しているため、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。Further, at that time, the adsorption tower is divided into a plurality of filling chambers along the exhaust gas passage direction, and the particle size of the activated carbon is increased in the filling chamber closer to the gas inlet, so that the exhaust gas treatment efficiency is further enhanced. The excellent effect that it can improve is acquired.
【図1】本発明に係る都市ゴミ焼却炉排ガス処理装置の
基本構成を示す概略構成図 [1] of the municipal solid waste incinerator exhaust gas treatment apparatus according to the present invention
Schematic diagram showing the basic configuration
【図2】前記基本構成の変形例の要部を示す概略構成図 FIG. 2 is a schematic configuration diagram showing a main part of a modified example of the basic configuration .
【図3】本発明の実施例に係る、吸着塔の要部を示す概
略構成図 FIG. 3 is a schematic configuration diagram showing a main part of an adsorption tower according to an embodiment of the present invention .
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/94 B03C 3/02 B B01D 53/36 102 F ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/94 B03C 3/02 B B01D 53/36 102 F
Claims (1)
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、 前記 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手段と、 切出した活性炭を前記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。1. An exhaust gas treatment device for an urban waste incinerator that removes harmful substances from the exhaust gas of an urban waste incinerator, and an electric dust collector that removes soot and dust from the exhaust gas, and means for injecting and mixing ammonia in the exhaust gas. The adsorption tower filled with activated carbon, which allows the exhaust gas after soot removal to pass through together with ammonia to adsorb and remove harmful substances in the exhaust gas, and the activated carbon in the adsorption tower, are substantially orthogonal to the passage direction of the exhaust gas. Direction, and means for cutting out outside the adsorption tower, a desorption tower for regenerating the cut out activated carbon, and means for returning the regenerated activated carbon into the adsorption tower , wherein the adsorption tower passes through the exhaust gas. It is divided into a plurality of filling chambers along the direction, and these filling chambers are filled with activated carbon with a larger particle size in order from the one closer to the exhaust gas inlet. And is moved in a direction substantially perpendicular to, and hand stage cut into each filling outdoor, after playing cut activated carbon in the desorption column, and means for classifying the grain each diameter, corresponding classified activated carbon to the particle diameter An exhaust gas treatment device for an urban refuse incinerator, characterized in that: means for returning to each of the filling chambers are installed.
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 JPH04277005A (en) | 1992-10-02 |
| JPH0779943B2 true 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) |
Families Citing this family (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 |
| JP3721247B2 (en) * | 1997-09-10 | 2005-11-30 | 住友重機械工業株式会社 | Low-temperature pyrolysis method for dioxins |
| DE102005005818A1 (en) * | 2005-02-08 | 2006-08-17 | Grochowski, Horst, Dr. | Process for purifying exhaust gases of a sintering process of ores in metal production |
| JP2007083221A (en) * | 2005-08-24 | 2007-04-05 | Jfe Steel Kk | Exhaust gas treatment method |
| JP4735353B2 (en) * | 2005-08-25 | 2011-07-27 | Jfeスチール株式会社 | Exhaust gas treatment method |
| JP4742926B2 (en) * | 2005-09-05 | 2011-08-10 | Jfeスチール株式会社 | Exhaust gas treatment equipment |
| WO2008071215A1 (en) * | 2006-12-14 | 2008-06-19 | Horst Grochowski | Method and device for scrubbing effluent gases from a sintering process for ores or other metal-containing materials in metal production |
| JP5285448B2 (en) * | 2009-01-23 | 2013-09-11 | 中部電力株式会社 | 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 |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4820368A (en) * | 1987-05-07 | 1989-04-11 | H. B. Fuller Company | Thermally stable reactive hot melt urethane adhesive composition having a thermoplastic polymer, a compatible, curing urethane polyalkylene polyol prepolymer and a tackifying agent |
-
1991
- 1991-03-01 JP JP5961491A patent/JPH0779943B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH04277005A (en) | 1992-10-02 |
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