JPH11141835A - Incinerator for removing harmful material - Google Patents
Incinerator for removing harmful materialInfo
- Publication number
- JPH11141835A JPH11141835A JP25051898A JP25051898A JPH11141835A JP H11141835 A JPH11141835 A JP H11141835A JP 25051898 A JP25051898 A JP 25051898A JP 25051898 A JP25051898 A JP 25051898A JP H11141835 A JPH11141835 A JP H11141835A
- Authority
- JP
- Japan
- Prior art keywords
- incinerator
- incineration
- air
- combustion chamber
- section
- 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
- 239000000463 material Substances 0.000 title claims abstract description 59
- 238000002485 combustion reaction Methods 0.000 claims abstract description 111
- 238000001035 drying Methods 0.000 claims abstract description 13
- 239000000126 substance Substances 0.000 claims description 82
- 238000010438 heat treatment Methods 0.000 claims description 16
- 238000007599 discharging Methods 0.000 claims description 6
- 239000000383 hazardous chemical Substances 0.000 claims 1
- 239000007789 gas Substances 0.000 abstract description 28
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 abstract description 24
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 15
- 229910052799 carbon Inorganic materials 0.000 abstract description 15
- 239000003546 flue gas Substances 0.000 abstract description 14
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 9
- 239000001301 oxygen Substances 0.000 abstract description 9
- 229910052760 oxygen Inorganic materials 0.000 abstract description 9
- 230000002950 deficient Effects 0.000 abstract description 4
- 239000000779 smoke Substances 0.000 description 57
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 15
- 229910002091 carbon monoxide Inorganic materials 0.000 description 11
- 238000010586 diagram Methods 0.000 description 11
- 239000010813 municipal solid waste Substances 0.000 description 9
- 238000007664 blowing Methods 0.000 description 8
- 238000005192 partition Methods 0.000 description 7
- 239000000428 dust Substances 0.000 description 6
- 239000003440 toxic substance Substances 0.000 description 6
- 231100000167 toxic agent Toxicity 0.000 description 5
- 238000009841 combustion method Methods 0.000 description 4
- 230000002093 peripheral effect Effects 0.000 description 4
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 231100000770 Toxic Equivalency Factor Toxicity 0.000 description 3
- 150000002013 dioxins Chemical class 0.000 description 3
- 230000001590 oxidative effect Effects 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- TXCDCPKCNAJMEE-UHFFFAOYSA-N dibenzofuran Chemical compound C1=CC=C2C3=CC=CC=C3OC2=C1 TXCDCPKCNAJMEE-UHFFFAOYSA-N 0.000 description 2
- 150000004826 dibenzofurans Chemical class 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 230000000391 smoking effect Effects 0.000 description 2
- 238000005979 thermal decomposition reaction Methods 0.000 description 2
- 238000009423 ventilation Methods 0.000 description 2
- 239000011800 void material Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical group Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 239000003818 cinder Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 1
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical compound S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 230000036962 time dependent Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Landscapes
- Incineration Of Waste (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、排煙中に含まれる有害
物質を取り除く焼却炉の改良に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an improvement of an incinerator for removing harmful substances contained in flue gas.
【0002】[0002]
【従来の技術】従来の焼却炉では、焼却炉内でバーナに
より被焼却物に点火し、空気を炉内に大量に送り込み被
焼却物を燃焼させていた。また、従来の焼却炉では、炉
内に送り込むことができる空気量に相当する被焼却物の
みしか炉内に投入することができない。2. Description of the Related Art In a conventional incinerator, an incinerator is ignited by a burner in the incinerator, and a large amount of air is sent into the incinerator to burn the incinerator. Further, in the conventional incinerator, only the incineration material corresponding to the amount of air that can be sent into the furnace can be introduced into the furnace.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、被焼却
物に点火し焼却炉内で燃焼させても、被焼却物内に空気
が万遍なく流れることがないとともに、被焼却物を投入
する度に焼却炉内の燃焼温度が下がり被焼却物が不完全
燃焼を起こし易い。そのために、一酸化炭素、ダイオキ
シン等の有害物質が大量に発生し、大気中に飛散すると
の欠点があった。また、焼却炉内に空気を強制的に送り
込み被焼却物を炉内で燃焼させる方式であるから、炉内
を加圧することとなるために部分的燃焼が激しく、乱流
になり煤塵等が大気中に飛散するとの欠点があった。However, even if the material to be incinerated is ignited and burned in an incinerator, air does not flow evenly in the material to be incinerated, and every time the material to be incinerated is charged. The combustion temperature in the incinerator decreases, and the incinerated matter is likely to cause incomplete combustion. For this reason, there is a disadvantage that harmful substances such as carbon monoxide and dioxin are generated in large amounts and scattered in the atmosphere. In addition, since air is forcibly sent into the incinerator and the incinerated material is burned in the furnace, the inside of the furnace is pressurized, so partial combustion is intense. There was a drawback that it scattered inside.
【0004】そこで、本発明は、一酸化炭素、ダイオキ
シン等の有害物質を排煙中に殆ど含まず、有害物質を大
気中に飛散させることがない有害物質を除去する焼却炉
を提供することを目的とするものである。Accordingly, an object of the present invention is to provide an incinerator which removes harmful substances such as carbon monoxide, dioxin and the like which are hardly contained in flue gas and do not scatter harmful substances into the atmosphere. It is the purpose.
【0005】[0005]
【課題を解決するための手段】本発明は、被焼却物を燃
焼させる焼却部に前記焼却部から発生する有害物質を除
去する除去部を連設し、吸引式負圧手段又は送風式負圧
手段により焼却部から除去部へ空気の流れをつくり、前
記焼却部内を常時負圧状態とすることを特徴とする有害
物質除去焼却炉の構成とした。According to the present invention, there is provided an incinerator for burning a substance to be incinerated, a removal unit for removing harmful substances generated from the incineration unit connected to the incineration unit, and a suction-type negative pressure means or a blast-type negative pressure. A means is provided to create a flow of air from the incineration section to the removal section, so that the inside of the incineration section is always kept in a negative pressure state.
【0006】[0006]
【実施例】本発明である有害物質除去焼却炉について、
図面に基づいて詳細に説明する。図1は、本発明である
有害物質除去焼却炉の第1実施例の縦断面図である。本
発明である有害物質除去焼却炉1は、生ゴミ4や一般焼
却ゴミである被焼却物5を焼却する焼却部2と、有害物
質を除去するための除去部2aから構成される。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Regarding the incinerator for removing harmful substances according to the present invention,
This will be described in detail with reference to the drawings. FIG. 1 is a longitudinal sectional view of a first embodiment of a toxic substance removing incinerator according to the present invention. The incinerator 1 for removing harmful substances according to the present invention includes an incinerator 2 for incinerating garbage 4 and incineration objects 5 which are general incineration trash, and a removing section 2a for removing harmful substances.
【0007】本有害物質除去焼却炉1の焼却部2は、一
次燃焼室9内で焼却され発生した焼却灰を受け入れる灰
受皿7が引き出し可能に収納されている灰受室8と、被
焼却物5を燃焼焼却する加熱バーナ12aを備えた一次
燃焼室9と、前記一次燃焼室9の上部に設けられた乾燥
室10からなる。図1中では加熱バーナ12aを示して
いるが、バーナのみに限定されるものではなく、ヒータ
を設置しても良く、またその他の熱源手段を設置しても
よい。前記加熱バーナ12aを設置しない構造であって
もよい。The incineration section 2 of the incinerator 1 for removing harmful substances comprises an ash receiving chamber 8 in which an ash tray 7 for receiving incinerated ash generated by being incinerated in the primary combustion chamber 9 is drawn out, and an incineration object. It comprises a primary combustion chamber 9 provided with a heating burner 12a for burning and incineration 5 and a drying chamber 10 provided above the primary combustion chamber 9. Although FIG. 1 shows the heating burner 12a, the invention is not limited to the burner alone, and a heater may be provided, or other heat source means may be provided. A structure without the heating burner 12a may be employed.
【0008】燃焼室9と乾燥室10間には空気を取り入
れるための多数の貫通孔10b、10b、10b、10
b、10b、・・・が形成されている仕切10aがあ
り、前記仕切10a上には水分を大量に含む生ゴミ4が
置かれる。A large number of through holes 10b, 10b, 10b, 10b for taking in air are provided between the combustion chamber 9 and the drying chamber 10.
There is a partition 10a in which b, 10b,... are formed, and the garbage 4 containing a large amount of water is placed on the partition 10a.
【0009】前記被焼却物5の燃焼により発生する燃焼
熱が、前記貫通孔10b、10b、10b、10b、1
0b、・・・を通り、仕切り10a上に置かれている水
分を大量に含んでいる生ゴミ4中の水分を蒸発させて乾
燥する。勿論、前記焼却部2には乾燥室10を設けない
構造としてもよい。前記仕切り10aの構造を皿状の仕
切りとしてもよく、また格子状の仕切りとしてもよい。The heat of combustion generated by the combustion of the incinerated material 5 is generated by the through holes 10b, 10b, 10b, 10b, 1b.
0b,..., The water in the garbage 4 containing a large amount of water placed on the partition 10a is evaporated and dried. Of course, the incineration unit 2 may have a structure in which the drying chamber 10 is not provided. The structure of the partition 10a may be a dish-shaped partition or a grid-shaped partition.
【0010】焼却部2の一次燃焼室9の火格子9aの近
接位置には、燃焼室9内の一般焼却ゴミである被焼却物
5を効率的に焼却するために、前記被焼却物5を焼却前
に着火し加熱しておくための加熱バーナ12aが設置さ
れている。前記加熱バーナ12aのようにバーナである
必要はなく、ヒータであってもよく、その他の加熱手段
であってもよい。In order to efficiently incinerate the incinerated material 5 which is general incineration garbage in the combustion chamber 9, the incinerated material 5 is placed at a position near the grate 9a in the primary combustion chamber 9 of the incineration section 2. A heating burner 12a for igniting and heating before incineration is provided. It does not need to be a burner like the heating burner 12a, and may be a heater or other heating means.
【0011】前記火格子9aの下方には、生ゴミ4及び
被焼却物5が焼却されることにより発生する焼却灰を受
け取る灰受皿7を灰受室8内に設けており、前記灰受室
8内の灰受皿7は、灰受室8から取り出し可能に設置さ
れるので、灰受皿7を取り出し灰受皿7に積もった焼却
灰を本焼却炉1外に取り出すことでができる。Below the grate 9a, an ash tray 7 for receiving incinerated ash generated by incinerating the garbage 4 and the incinerated material 5 is provided in an ash receiving chamber 8. The ash tray 7 inside the ash tray 8 is installed so as to be able to be taken out of the ash receiving chamber 8, so that the ash tray 7 can be taken out and the incineration ash accumulated on the ash tray 7 can be taken out of the incinerator 1.
【0012】前記灰受皿7に代わりに、焼却灰を搬出す
る手段として振動式コンベアーベルト、回転式コンベア
ーベルト等を設置してもよく、落下した焼却灰を吸引す
る手段により取り出す構造としてもよい。Instead of the ash tray 7, a vibrating conveyor belt, a rotary conveyor belt, or the like may be provided as a means for carrying out the incinerated ash, and a structure may be employed in which the dropped incinerated ash is taken out by means of suction.
【0013】図1に示すように、本焼却炉1の除去部2
aは、焼却部2より排出される未燃ガスを焼却するため
の加熱バーナ12が設置されている二次燃焼室11と、
焼却部2の灰受室8と一次燃焼室9と乾燥室10内を常
時負圧状態とするファン3とから構成されている。符号
13は、二次燃焼室11により未燃ガスが燃焼され、大
気中に排出するための排煙口13である。勿論、前記加
熱バーナ12を、ヒータ、その他の加熱手段としてもよ
い。As shown in FIG. 1, the removing section 2 of the incinerator 1
a is a secondary combustion chamber 11 in which a heating burner 12 for incinerating unburned gas discharged from the incineration section 2 is installed;
The ash receiving chamber 8, the primary combustion chamber 9 and the drying chamber 10 of the incineration unit 2 are constituted by a fan 3 which always keeps the inside of the drying chamber 10 in a negative pressure state. Reference numeral 13 denotes a smoke outlet 13 for burning unburned gas by the secondary combustion chamber 11 and discharging the unburned gas into the atmosphere. Of course, the heating burner 12 may be a heater or other heating means.
【0014】焼却部2内を常時負圧状態にしておく手段
としては、図1に示すように、除去部2aにファン3を
設置して、ファン3を回転させて焼却部2内の燃焼熱気
を吸い込むようにして焼却部2内を負圧状態にする吸引
式負圧手段と図2に示すようにブロワー3aにより二次
燃焼室11内の排煙筒3b内に空気を強制的に送り込
み、送り込まれた空気の流れに二次燃焼室11内の煙り
を便乗させて排出させることにより焼却部2内を負圧状
態とする送風式負圧手段とがある。As a means for keeping the inside of the incineration unit 2 in a negative pressure state, as shown in FIG. 1, a fan 3 is installed in the removal unit 2a, and the fan 3 is rotated to burn hot air in the incineration unit 2. Air is forcibly fed into the smoke stack 3b in the secondary combustion chamber 11 by the suction type negative pressure means for sucking air and bringing the inside of the incineration section 2 into a negative pressure state, and the blower 3a as shown in FIG. There is a ventilation-type negative pressure means that makes the inside of the incineration section 2 a negative pressure state by piggybacking the smoke in the secondary combustion chamber 11 on the flow of the discharged air and discharging the smoke.
【0015】焼却炉2の一次燃焼室9及び乾燥室10内
では、炉床6に形成されている空気取入孔6a、6a、
6a、6a、6a、・・・から取り込まれた空気が、除
去部2aのファン3により、常時、矢印A方向に送り出
されているので、空気は空気取入孔6a、6a、6a、
6a、6a→灰受室8→一次燃焼室9→乾燥室10→二
次燃焼室11→ファン3→排煙口13のように一定の方
向に流れており、焼却部2内が常時負圧に保たれてい
る。ファン3は吸引式負圧手段であるが、送風式負圧手
段としてもよい。In the primary combustion chamber 9 and the drying chamber 10 of the incinerator 2, air intake holes 6a, 6a formed in the hearth 6 are provided.
Since the air taken in from 6a, 6a, 6a,... Is always sent out in the direction of arrow A by the fan 3 of the removing unit 2a, the air is taken into the air intake holes 6a, 6a, 6a,.
6a, 6a → ash receiving chamber 8 → primary combustion chamber 9 → drying chamber 10 → secondary combustion chamber 11 → fan 3 → smoke outlet 13 flows in a certain direction, and the inside of the incineration unit 2 is always under negative pressure. It is kept in. The fan 3 is a suction-type negative pressure means, but may be a blow-type negative pressure means.
【0016】本有害物質除去焼却炉1の除去部2aに設
置されているファン3の回転速度は調節することがで
き、ファン3の回転速度を調節することにより、炉床6
の空気取入孔6aから灰受室8、一次燃焼室9及び乾燥
室10内に取り込む空気量を微妙に調節することができ
る。このように、ファン3の回転速度を調節することに
より焼却部2内に取り込む空気量を制御することができ
るので、焼却部2内の酸素を必要最小限に押さえること
ができる。The rotation speed of the fan 3 installed in the removal section 2a of the incinerator 1 for removing harmful substances can be adjusted, and by adjusting the rotation speed of the fan 3, the hearth 6 can be adjusted.
The amount of air taken into the ash receiving chamber 8, the primary combustion chamber 9, and the drying chamber 10 from the air intake hole 6a can be finely adjusted. As described above, since the amount of air taken into the incineration unit 2 can be controlled by adjusting the rotation speed of the fan 3, oxygen in the incineration unit 2 can be suppressed to a minimum.
【0017】焼却部2内に生ゴミ4及び被焼却物5を満
杯に詰め燃焼させると、吸引した空気分だけ下層部より
燃焼して行き、上層部は酸欠状態となり、焼却部2内に
は、未燃ガスと未燃カーボンが大量に発生し、還元雰囲
気下となる。還元雰囲気下では一酸化炭素とダイオキシ
ン等の有害物質の発生を抑えることができ、この還元雰
囲気下の状態は酸素を薄く、300℃以上500℃で焼
却するとダイオキシン、窒素酸化物、硫黄酸化物、塩化
水素が熱分解されるため排煙中にはダイオキシン、NO
x、SOx、HCL等の有害物質が非常に少なくなる。When the garbage 4 and the incineration material 5 are filled and burned in the incineration unit 2, the air is burned from the lower part by the amount of the sucked air, and the upper part becomes oxygen-deficient. As a result, a large amount of unburned gas and unburned carbon are generated, and the atmosphere is reduced. Under a reducing atmosphere, it is possible to suppress the generation of harmful substances such as carbon monoxide and dioxin. In this reducing atmosphere, oxygen is thin, and when incinerated at 300 ° C. or more and 500 ° C., dioxin, nitrogen oxide, sulfur oxide, Dioxin, NO in flue gas due to thermal decomposition of hydrogen chloride
Toxic substances such as x, SOx, HCL, etc. are extremely reduced.
【0018】還元雰囲気下の未燃ガスや未燃カーボン等
を二次燃焼室11でバーナ12を点火し、前記未燃ガス
及び未燃カーボン等を約800℃以上の高温で焼却する
と、前記未燃ガス及び未燃カーボン等が前記未燃ガス及
び未燃カーボン等に含まれる一酸化炭素又はダイオキシ
ン等を発生させることなく熱分解し除去され、排煙口1
3からは還元雰囲気下で排煙中に含まれていた前記有害
物質が完全に取り除かれて排煙口13から排出される。
前記バーナ12は、バーナのみに限定されるものではな
く、ヒータを設置しても良く、またその他の熱源手段を
設置してもよい。When the burner 12 ignites unburned gas or unburned carbon in a reducing atmosphere in the secondary combustion chamber 11 and incinerates the unburned gas or unburned carbon at a high temperature of about 800 ° C. or more, The burned gas and unburned carbon are thermally decomposed and removed without generating carbon monoxide or dioxin contained in the unburned gas and unburned carbon, and the exhaust gas 1
From 3, the harmful substances contained in the flue gas are completely removed under the reducing atmosphere and discharged from the flue gas outlet 13.
The burner 12 is not limited to the burner alone, but may be provided with a heater or other heat source means.
【0019】一酸化炭素又はダイオキシン等の有害物質
を除去するための、二次燃焼室11で焼却する最も好ま
しい温度は約800℃以上の高温で焼却することであ
り、この温度の還元雰囲気下で排煙中に含まれていた未
燃ガス、一酸化炭素等の有害物質が効率的に熱分解し除
去される。The most preferable temperature for incineration in the secondary combustion chamber 11 for removing harmful substances such as carbon monoxide or dioxin is to incinerate at a high temperature of about 800 ° C. or more, and in a reducing atmosphere at this temperature. Harmful substances such as unburned gas and carbon monoxide contained in the flue gas are efficiently thermally decomposed and removed.
【0020】図2は本発明である有害物質除去焼却炉の
第2実施例の縦断面図である。本例の有害物質除去焼却
炉1aでは、焼却部2の構成は図1に示した構成と同様
であるが、除去部2aの構成が異なる。そして、本例で
は焼却部2内を負圧状態にする手段としてはブロワーに
よる「送風式負圧手段」を採用している。FIG. 2 is a longitudinal sectional view of a second embodiment of the incinerator for removing harmful substances according to the present invention. In the harmful substance removal incinerator 1a of this example, the configuration of the incineration unit 2 is the same as the configuration shown in FIG. 1, but the configuration of the removal unit 2a is different. In this example, as a means for bringing the inside of the incineration unit 2 into a negative pressure state, a "blowing negative pressure means" using a blower is employed.
【0021】即ち、除去部2aは、排煙筒11aを内設
するとともにバーナ12を備えた二次燃焼室11と、送
風用のファン3を内蔵するブロワー3aとから構成され
ている。排煙筒11aの下端の近接位置にブロワー3a
の先端部3bが位置するように設置されている。また
は、先端部3bは排煙筒11aの下端の中央位置に近接
させることがよい。バーナ12は、バーナに限定され
ず、ヒータでもよく、またその他の加熱手段としてもよ
い。That is, the removing section 2a comprises a secondary combustion chamber 11 provided with a smoke exhaust tube 11a and a burner 12, and a blower 3a having a fan 3 for blowing air therein. The blower 3a is located near the lower end of the smoke stack 11a.
Is disposed so that the tip 3b of the is located. Alternatively, the tip 3b may be located close to the center of the lower end of the smoke stack 11a. The burner 12 is not limited to a burner, and may be a heater or other heating means.
【0022】前記ブロワー3a内のファン3を駆動し回
転させることにより矢印B方向に外気をブロワー3a内
に取り込み、取り込まれた空気は二次燃焼室11内の排
煙筒11a内に送り出される際に、前記送風による負圧
から二次燃焼室11のバーナ12によって焼却された煙
りを伴って、二次燃焼室11内の煙りは排煙筒11a内
を通って矢印Cに示す方向に排出される。By driving and rotating the fan 3 in the blower 3a, outside air is taken into the blower 3a in the direction of arrow B. When the taken air is sent out to the smoke exhaust tube 11a in the secondary combustion chamber 11, The smoke in the secondary combustion chamber 11 is discharged in the direction shown by the arrow C through the smoke exhaust tube 11a, together with the smoke incinerated by the burner 12 of the secondary combustion chamber 11 from the negative pressure due to the blowing.
【0023】本例の有害物質除去焼却炉1aでは、焼却
部2内で発生した有害物質を含む未燃ガス、未燃カーボ
ン等からなる煙を焼却部2に連設されている除去部2a
の二次燃焼室11にファン3の駆動により排煙室11a
内に取り込み、二次燃焼室11内で未燃ガス及び未燃カ
ーボン等の有害物質を含む還元雰囲気下で燃焼させて、
排煙筒11aより有害物質を分解し除去した煙りを大気
中に放出する。In the incinerator 1a for removing harmful substances according to the present embodiment, the removal section 2a connected to the incineration section 2 is provided with smoke composed of unburned gas, unburned carbon and the like containing harmful substances generated in the incineration section 2.
The fan 3 drives the secondary combustion chamber 11 into a smoke exhaust chamber 11a.
And burned in a reducing atmosphere containing harmful substances such as unburned gas and unburned carbon in the secondary combustion chamber 11,
The smoke emitted from the smoke stack 11a, which decomposes and removes harmful substances, is released into the atmosphere.
【0024】図3は、本発明である有害物質除去焼却炉
の第3実施例の縦断面図である。本例の有害物質除去焼
却炉1bでは、二次燃焼室11に2基のバーナ12、1
2を設置した構成の有害物質除去焼却炉1bである。こ
のように、二次燃焼室11に2基のバーナ12、12を
設置し燃焼させることにより、より効率的に有害物質を
含む未燃ガス及び未燃カーボン等からなる還元雰囲気下
で図3中のDにおいて焼却し、熱分解させることが可能
となる。図3中では、二次燃焼室11に2基のバーナ1
2、12のみが設置されているが、2基以上複数のバー
ナを設置してもよい。FIG. 3 is a longitudinal sectional view of a third embodiment of the incinerator for removing harmful substances according to the present invention. In the harmful substance removal incinerator 1b of this example, two burners 12, 1
2 is a harmful substance removal incinerator 1b having a configuration 2 installed. In this way, by installing and burning two burners 12, 12 in the secondary combustion chamber 11, more efficiently under the reducing atmosphere composed of unburned gas and unburned carbon containing harmful substances in FIG. Incineration and thermal decomposition can be performed at D. In FIG. 3, two burners 1 are provided in the secondary combustion chamber 11.
Although only 2 and 12 are installed, two or more burners may be installed.
【0025】本例の有害物質除去焼却炉1bでは、ファ
ン3を駆動させ回転させると、二次燃焼室11の煙りは
矢印A方向に流れ、焼却部2内の空気は、ファン3によ
り空煙りが吸引されるために灰受室8→一次燃焼室9→
乾燥室10→二次燃焼室11の順に流れる。そのため
に、焼却部2内に充満している未燃ガス及び未燃カーボ
ン等の有害物質を含む煙り(排気ガス)が、負圧状態と
なっている二次燃焼室11に取り込まれ、バーナ12、
12により煙りに含まれている有害物質を焼却して排煙
口13から排出される。本例では、吸引式負圧手段を採
用している。In the harmful substance removing incinerator 1b of this embodiment, when the fan 3 is driven and rotated, the smoke in the secondary combustion chamber 11 flows in the direction of arrow A, and the air in the incineration section 2 is emptied by the fan 3 Ash receiving chamber 8 → primary combustion chamber 9 →
It flows from the drying chamber 10 to the secondary combustion chamber 11 in this order. For this purpose, smoke (exhaust gas) containing harmful substances such as unburned gas and unburned carbon filled in the incineration section 2 is taken into the secondary combustion chamber 11 in a negative pressure state, and burners 12. ,
The harmful substances contained in the smoke are incinerated by 12 and discharged from the smoke outlet 13. In this example, suction type negative pressure means is employed.
【0026】図4及び図5は、空気を吹き込む場合と空
気を吸引する場合に、空気が被焼却物に対しどのような
流れをするかを示した図である。図4は、ファン14を
回転させ被焼却物に空気を当てて「空気を吹き込む場
合」に被焼却物の外周の空気の流れる状態を示した図で
ある。図5はファン14を回転させ「空気を吸引する場
合」に被焼却物の外周の空気の流れる状態を示した図で
ある。図4は従来の焼却炉内での空気の流れ方、即ち、
「空気を送り込む場合」を示した図であり、図5は本発
明である有害物質除去焼却炉のように「空気を取り込む
場合」の空気の流れ方を示した図である。FIG. 4 and FIG. 5 are views showing how air flows into an incineration object when air is blown and air is sucked. FIG. 4 is a diagram showing a state in which air flows around the incineration object when the fan 14 is rotated and air is applied to the incineration object to blow air. FIG. 5 is a diagram showing a state in which the air flows around the incineration object when the fan 14 is rotated and the air is sucked. FIG. 4 shows the flow of air in a conventional incinerator, that is,
FIG. 5 is a diagram illustrating “when air is supplied”, and FIG. 5 is a diagram illustrating a flow of air when “when air is supplied” as in the incinerator for removing harmful substances according to the present invention.
【0027】従来の焼却炉の空気の流れ方を示した図4
では、ファン14の回転によって空気を物体(被焼却
物)に向かって吹き付けると、空気は矢印Eに示すよう
に物体15の前面15aに当たり、空気は層流から乱流
になり物体15の上面と下面に別れて流れ、物体(被焼
却物)15の背面15bには空気は流れ込むことはな
い。FIG. 4 shows the flow of air in a conventional incinerator.
Then, when the air is blown toward the object (incineration object) by the rotation of the fan 14, the air hits the front surface 15a of the object 15 as shown by an arrow E, and the air changes from laminar flow to turbulent flow, and Air does not flow into the back surface 15b of the object (incineration object) 15 by flowing to the lower surface.
【0028】そのために、空気は物体15の前面のみに
当たり、物体(被焼却物)15の背面15bには空気が
当たることがなく、被焼却物15の背面には新しい空気
が流れることがないため、被焼却物15の背面15b部
分が未燃焼部分となり焼却されず残存してしまう。加圧
のため被焼却物15の空隙には圧力損失及び閉塞するた
めに奥まで空気が届かず未燃焼部分が残存する。For this reason, the air hits only the front surface of the object 15, the air does not hit the back surface 15 b of the object (incineration object) 15, and no new air flows on the back surface of the incineration object 15. However, the back surface 15b of the incinerated material 15 becomes an unburned portion and remains without being incinerated. Due to the pressurization, air does not reach the interior due to pressure loss and blockage due to pressure loss and clogging, and unburned portions remain.
【0029】図5はファン14を駆動し回転させ「空気
を吸引する場合」による際の被焼却物の外周の空気が流
れる状態を示した図である。本発明である有害物質除去
焼却炉1、1a、1b内の空気の流れ方を示した図5で
は、ファン14の回転により、空気を吸引し、吸引され
た空気は矢印F方向に流れる。このとき被焼却物15の
前面15a、背面15b、下面及び下面の全外周面に万
遍なく新しい空気が当たるので、空気を吸引している状
態で被焼却物15を燃焼させれば被焼却物15は完全燃
焼するものである。また、このような空気を吸引してい
る状態、即ち、焼却部部2内を負圧状態として被焼却物
15を燃焼させると被焼却物20自体の空隙にも微量の
空気が流れるので被焼却物15に未燃焼部分が残存する
ことが無く完全燃焼する。FIG. 5 is a view showing a state in which the air around the incineration object flows when the fan 14 is driven to rotate and the air is sucked. In FIG. 5 showing the flow of air in the harmful substance removal incinerator 1, 1a, 1b of the present invention, air is sucked by the rotation of the fan 14, and the sucked air flows in the direction of arrow F. At this time, new air uniformly hits the entire outer peripheral surface of the front surface 15a, the back surface 15b, the lower surface, and the lower surface of the incinerated material 15. Therefore, if the incinerated material 15 is burned while the air is being sucked, the incinerated material is Numeral 15 indicates a complete combustion. Further, when the incinerated material 15 is burned in a state in which such air is sucked, that is, the inside of the incineration unit 2 is in a negative pressure state, a small amount of air also flows into the void of the incinerated material 20 itself, so that incineration is performed. The product 15 is completely burned without an unburned portion remaining.
【0030】図6は本発明である有害物質除去焼却炉の
焼却部内の温度の経時変化を示した表である。図2を参
照しながら説明すると、一次燃焼室出口温度曲線16は
図2のG点で測定したものであり、二次燃焼室上部温度
曲線17は図2のH点で測定したものである。FIG. 6 is a table showing the change over time in the temperature in the incinerator of the incinerator for removing harmful substances according to the present invention. Referring to FIG. 2, the primary combustion chamber outlet temperature curve 16 is measured at point G in FIG. 2, and the secondary combustion chamber upper temperature curve 17 is measured at point H in FIG.
【0031】一次燃焼室出口温度が450度未満の期間
18は、ダイオキシン等の有害物質が分解されずに排煙
中に含まれるため、二次燃焼室11内のバーナ12を点
火し、有害物質を燃焼させ排煙中から取り除く。During the period 18 when the outlet temperature of the primary combustion chamber is lower than 450 ° C., since the harmful substances such as dioxin are contained in the exhaust gas without being decomposed, the burner 12 in the secondary combustion chamber 11 is ignited and the harmful substances are ignited. Burn and remove from smoke.
【0032】一次燃焼室の出口温度が450度以上の期
間19は、一次燃焼室9内の空気量が必要最小限に抑え
られているため、焼却部2内に被焼却物20を満杯に詰
め燃焼させると、吸引した空気量だけ下層部より燃焼し
ていき、上層部は酸欠状態となり、一次燃焼室9内の未
燃ガス及び未燃カーボンが発生した状態である還元雰囲
気下で二次燃焼室において燃焼され、ダイオキシン、一
酸化炭素の発生が抑えられると共に、これらの有害物質
が分解されるため排煙中に含まれない。During the period 19 in which the outlet temperature of the primary combustion chamber is 450 ° C. or more, since the amount of air in the primary combustion chamber 9 is kept to a necessary minimum, the incineration unit 2 is filled with the incineration material 20 completely. When the fuel is burned, it burns from the lower part by the amount of the sucked air, the upper part becomes oxygen-deficient, and the secondary part in the reducing atmosphere where unburned gas and unburned carbon are generated in the primary combustion chamber 9. It is burned in the combustion chamber, and the generation of dioxin and carbon monoxide is suppressed, and these harmful substances are decomposed so that they are not included in the flue gas.
【0033】図7は本発明である有害物質除去焼却炉に
より被焼却物を焼却した焼却炉の排煙中に含まれるダイ
オキシンとジベンゾフランの濃度と毒性等量濃度を示し
た表である。FIG. 7 is a table showing concentrations of dioxins and dibenzofurans and toxic equivalents contained in flue gas of an incinerator in which incinerators are incinerated by the incinerator for removing harmful substances according to the present invention.
【0034】図7に示すように、本発明である有害物質
除去焼却炉1、1a、1bでは、ダイオキシンの毒性等
量濃度は0.031ng/m3であり、前記濃度は平成
9年12月1日から改正施行される大気汚染防止法と廃
棄物処理法で定められている基準である0.1ng/m
3を下回っているとの測定結果を得ている。また、ジベ
ンゾフランの排出量もまた極めて少ない。As shown in FIG. 7, in the incinerator for removing harmful substances 1, 1a and 1b of the present invention, the toxic equivalent concentration of dioxin is 0.031 ng / m 3 , and said concentration is in December 1997. 0.1ng / m, which is the standard stipulated by the Air Pollution Control Law and the Waste Management Law, which is revised and enforced from 1st
The result of the measurement that it is less than 3 has been obtained. Dibenzofuran emissions are also very low.
【0035】図8は従来の焼却炉内の空気の流れ方を示
した図、即ち、空気を吹き込み被焼却物に空気を当てる
構造の焼却炉内の被焼却物と空気の流れを示した図であ
る。図9は本発明である有害物質除去焼却炉内の空気の
流れ方を示した図、即ち、空気を吸引して被焼却物に空
気を当てる構造の焼却炉内の被焼却物と空気の流れを示
した図である。FIG. 8 is a diagram showing a flow of air in a conventional incinerator, that is, a diagram showing an incinerator and a flow of air in an incinerator having a structure in which air is blown and air is applied to the incinerator. It is. FIG. 9 is a view showing the flow of air in the incinerator for removing harmful substances according to the present invention, that is, the flow of air and the incinerator in the incinerator having a structure in which air is sucked and air is applied to the incinerator. FIG.
【0036】従来のようなブロワー等により被焼却物に
空気を吹き込み被焼却物15を焼却する場合には、焼却
炉2の燃焼室9cで被焼却物15を燃焼させるのには粉
砕した被焼却物に着火し、着火面に向かってファン14
等で送風14aし、被焼却物15に強制的に直接空気を
当て、燃焼状態を確認しながら燃焼させていた。このよ
うにブロワーのファン14による送風14aのため空気
が直接被焼却物15に当たる前面15aだけは良く燃焼
する。また、前記送風の空気により被焼却物前面15a
より被焼却物15内部に向かってほんの僅かであるが徐
々に内部に燃焼部分15cが進行する。In the case where the incinerated material 15 is incinerated by blowing air into the incinerated material by a conventional blower or the like, the pulverized incinerated material is required to burn the incinerated material 15 in the combustion chamber 9c of the incinerator 2. The object is ignited and the fan 14
For example, the air is blown 14a and the air is forcibly and directly applied to the incineration object 15 to burn while checking the combustion state. In this way, only the front surface 15a where the air directly hits the incineration object 15 burns well due to the blowing 14a by the blower fan 14. In addition, the air blown by the air blows the front surface 15a of the object to be incinerated.
The combustion portion 15c proceeds slightly but gradually toward the inside of the incineration object 15.
【0037】しかし、送風した空気が当たらない部分、
つまり被焼却物15の背面15bでは、被焼却物前面1
5aにおいて燃焼させた後の空気が被焼却物背面15b
に廻ることもあって酸素が薄く、被焼却物15の背後は
通常乱流14bが発生し空気が薄くなると共に、被焼却
物15の背面15bに燃焼部分があってもその燃焼を物
体内部に進行させるように空気が閉塞し吹きつけないた
め燃焼部分が被焼却物15の内部に進行しない。However, the part where the blown air does not hit,
In other words, on the back surface 15b of the incinerated material 15,
The air after burning in 5a is the back surface 15b of the incinerated material.
The turbulence 14b is usually generated behind the incineration object 15 and the air becomes thinner, and even if there is a burning part on the back surface 15b of the incineration object 15, the combustion is transferred to the inside of the object. Since the air is blocked and does not blow so as to proceed, the burning portion does not proceed into the incineration object 15.
【0038】そのために、図8に示すように、被焼却物
15のほとんどが完全燃焼して灰になることはなく、特
に、被焼却物15に未燃焼部分15dが多く残ってしま
う。このように従来の空気を吹き付ける方式により燃焼
させる方法では、被焼却物15から有害物質を発生させ
ない条件として通常知られているところの完全燃焼とい
う条件を満たせなくなってしまう。As a result, as shown in FIG. 8, most of the incinerated material 15 is not completely burned to ash, and particularly, a large amount of unburned portion 15d remains in the incinerated material 15. As described above, the conventional method of burning by air blowing cannot satisfy the condition of complete combustion, which is generally known as a condition that does not generate harmful substances from the incineration object 15.
【0039】ところが、図9に示すように、本発明であ
る有害物質除去焼却炉では被焼却物15を燃焼させるの
に被焼却物15に直接空気を当てず、ファン14を駆動
回転させて空気を一次燃焼室9内に吸引する方法(吸引
式負圧手段)により負圧状態にすると、焼却部2内が負
圧状態となるために、空気が取込口外の無限空間から取
り込まれた空気は、直接に、被焼却物15に当たらず、
吸引取り込まれた空気14cは被燃焼物15の外周面全
面に空気が万遍なく流れる。However, as shown in FIG. 9, in the incinerator for removing harmful substances according to the present invention, air is not directly applied to the incinerated material 15 to burn the incinerated material 15 but the fan 14 is driven and rotated to rotate the air. When the air is sucked into the primary combustion chamber 9 (suction-type negative pressure means), the inside of the incinerator 2 is in a negative pressure state, so that air is taken in from the infinite space outside the inlet. Does not directly hit the incineration material 15,
The air 14c sucked and taken in flows uniformly over the entire outer peripheral surface of the burnable object 15.
【0040】このため、負圧状態によって被焼却物15
の背面15bに乱流を起こすこともなく、被焼却物15
の外周面全面を空気が滑らかに流れると共に、被焼却物
15の前面15aにある燃焼部分が被焼却物15の内部
の空隙にも微量の空気が流れるので周囲に向かって確実
に進行し完全に燃焼する。For this reason, the incineration material 15 depends on the negative pressure state.
Turbulence does not occur on the back surface 15b of the
The air smoothly flows over the entire outer peripheral surface of the incineration object 15, and a small amount of air flows through the combustion portion on the front surface 15a of the incineration object 15 into the void inside the incineration object 15, so that the air proceeds reliably toward the surroundings and completely. Burn.
【0041】前記一次焼却室9内が負圧状態となり、空
気を空気取込口から取り込む(吸引する)ので、被焼却
物15の外周面全面は勿論のこと、被焼却物15の内部
にある僅かな隙間15eを通って空気が行き渡り、被焼
却物15内部より全体が万遍なく燃焼し、完全に灰にな
るまで燃焼してしまう。Since the inside of the primary incineration chamber 9 is in a negative pressure state and air is taken in (sucked) from the air intake port, not only the entire outer peripheral surface of the incineration object 15 but also the inside of the incineration object 15 is present. The air spreads through the small gap 15e, and the whole is burned evenly from the inside of the incineration object 15 and burned until it completely becomes ash.
【0042】図9に示すような理由により、被焼却物1
5のほとんどが完全燃焼して灰になり、被焼却物が灰に
なるまで完全に燃焼する。このように本発明による空気
を吸引する場合方法により負圧状態を利用した燃焼方法
によって、被焼却物15から有害物質を発生させない条
件として通常知られているところの完全燃焼という条件
を満たすことができる。For the reasons shown in FIG.
Most of 5 is completely burned to ash, and the incinerated matter is completely burned to ash. As described above, the method of sucking air according to the present invention satisfies the condition of complete combustion, which is generally known as a condition that does not generate harmful substances from the incineration object 15, by the combustion method using a negative pressure state. it can.
【0043】実際に、使用済みの会計伝票、約1m×
0.5mの上質ロール紙、生ゴミ等を本発明である有害
物質除去焼却炉の一次燃焼室9に粉砕せず密に詰め込ん
で燃焼実験してみたところ、煙突より出る煙はほとんど
なく、また、被焼却物の焼却後の焼却灰も白くなるまで
完全に燃焼しきっていた。特に、隙間がほとんど全く無
い上質ロール紙にクレータ状の穴が開き、空気が間隙を
通り抜けるので燃え残りが全くなく完全に燃焼して白い
焼却灰になったことから、本焼却炉の負圧を利用した燃
焼方法が従来のものより格段に良いことを実験によって
確認した。Actually, a used accounting slip, about 1 m ×
When a 0.5 m high-quality roll paper, garbage, etc. were densely packed without crushing into the primary combustion chamber 9 of the incinerator for removing harmful substances according to the present invention, there was almost no smoke emitted from the chimney. After the incineration of the incinerated material, the incineration ash was completely burned until it turned white. In particular, since a crater-shaped hole was opened in high-quality roll paper with almost no gap, and air passed through the gap, there was no unburned part, and it burned completely and turned into white incinerated ash. Experiments have shown that the combustion method used is much better than the conventional one.
【0044】図10、図11、図12、図13、図14
及び図15は、本発明である有害物質除去焼却炉の焼却
部内で被焼却物の燃焼状態を示した図である。即ち、図
10から図15は、本焼却炉の一次焼却室9内に置かれ
た被焼却物20がどのような状態で燃焼していくかを順
次示した図である。FIGS. 10, 11, 12, 13, and 14
And FIG. 15 is a diagram showing a combustion state of the incineration material in the incineration section of the incinerator for removing harmful substances according to the present invention. That is, FIGS. 10 to 15 are diagrams sequentially showing in what state the incinerated material 20 placed in the primary incineration chamber 9 of the present incinerator burns.
【0045】図10から図15に示す焼却部2は乾燥室
10が無い構造の焼却部であり、図1、図2及び図3に
示した焼却部の一次燃焼室9と同一構造である。貫通孔
9b、9b、9b、9b、9b、・・・が形成される火
格子9aにより、一次燃焼室9と灰受室8とに分かれて
いる。前記一次燃焼室9の上端には排煙を排出する燃焼
室出口9dを設けると共に、空気を取り入れるための多
数の空気取入孔6a、6a、6a、6a、6a、・・・
が形成されている炉床6と、前記火格子9aとの間にあ
る灰受室8内に被焼却物20が焼却されることにより発
生する焼却灰を受け取る灰受皿7を取り出し可能に設け
たものである。The incineration section 2 shown in FIGS. 10 to 15 is an incineration section having no drying chamber 10 and has the same structure as the primary combustion chamber 9 of the incineration section shown in FIGS. 1, 2 and 3. Are divided into a primary combustion chamber 9 and an ash receiving chamber 8 by a grate 9a in which through holes 9b, 9b, 9b, 9b, 9b,... Are formed. At the upper end of the primary combustion chamber 9, there is provided a combustion chamber outlet 9d for discharging smoke and a large number of air intake holes 6a, 6a, 6a, 6a, 6a,.
The ash tray 7 for receiving incinerated ash generated by incineration of the incinerated material 20 in the ash receiving chamber 8 between the hearth 6 in which the ash is formed and the grate 9a is provided so as to be able to be taken out. Things.
【0046】図10から図15では、被焼却物15に加
熱着火した状態から説明するので、図1lから図15に
示した焼却部2には加熱バーナ12a、ヒータ等の熱源
等を表示していない。FIGS. 10 to 15 show the state in which the incineration object 15 is heated and ignited. Therefore, the incineration section 2 shown in FIGS. 11 to 15 shows a heating source such as a heating burner 12a and a heater. Absent.
【0047】先ず、図10に示すように、本焼却部2の
一次燃焼室9内に被焼却部20が積み上げられ、被焼却
物20の下部に点火する。点火すると、前記被焼却物2
0の下部は酸化燃焼部20bで貫通孔9b、9b、9
b、9b、9b、・・・より取り込まれる空気中の酸素
と共に被焼却物20が燃焼する。前記酸化燃焼部20b
の上には、全く燃焼しない状態の未燃焼部20aが存在
する。First, as shown in FIG. 10, the incineration unit 20 is stacked in the primary combustion chamber 9 of the main incineration unit 2, and the lower part of the incineration object 20 is ignited. When ignited, the incinerated material 2
The lower part of 0 is an oxidation combustion part 20b and the through holes 9b, 9b, 9
b, 9b, 9b,... and the oxygen in the air taken in, the incinerated material 20 burns. The oxidation combustion section 20b
There is an unburned portion 20a that does not burn at all.
【0048】焼却部2の上部に形成されている燃焼室出
口9dは、図1から図3で示した本発明である有害物質
除去焼却炉を構成する有害物質を除去する除去部2aに
連設されており、前記除去部2a内に設けられたファン
3が回転することにより空気が焼却部2内に吸引され取
り込まれる。The combustion chamber outlet 9d formed above the incineration unit 2 is connected to the removal unit 2a for removing harmful substances constituting the harmful substance removal incinerator according to the present invention shown in FIGS. 1 to 3. The air is sucked into the incineration unit 2 by the rotation of the fan 3 provided in the removal unit 2a.
【0049】吸引口9dから一次燃焼室9内の熱気が吸
引されることで、前記一次燃焼室9内は負圧状態とな
り、空気取込孔6a、6a、6a、6a、6a、・・・
を通って貫通孔9b、9b、9b、9b、9b、・・・
より新鮮な空気が吸引される。When the hot air in the primary combustion chamber 9 is sucked from the suction port 9d, the inside of the primary combustion chamber 9 is in a negative pressure state, and the air intake holes 6a, 6a, 6a, 6a, 6a,.
Through the through holes 9b, 9b, 9b, 9b, 9b, ...
Fresher air is aspirated.
【0050】新鮮な空気は、被焼却物20内の酸化燃焼
部20b及び未燃焼部20aの隙間を通過して被焼却物
20の上方に抜ける。前記新鮮な空気が前記被焼却物2
0の下部にある酸化燃焼部20bを通過する際、前記被
焼却物20内を通過する新鮮な空気は酸化燃焼を促進さ
せると共に、煙をたっぷり含んで未燃焼部20aを通過
し被焼却物20上方に抜け出る。The fresh air passes through the gap between the oxidized combustion part 20b and the unburned part 20a in the incineration material 20, and escapes above the incineration material 20. The fresh air is the incinerated material 2
When passing through the oxidized combustion section 20b at the lower portion of the incinerator 20, the fresh air passing through the incinerated substance 20 promotes oxidative combustion, and also contains plenty of smoke, passes through the unburned section 20a, and Get out upwards.
【0051】前記被焼却物20上方に抜け出た煙をたっ
ぷり含んだ熱気内には一酸化炭素又はダイオキシン等の
有害物質が還元雰囲気下で熱分解し微量に混在している
が、燃焼させることによって一酸化炭素又はダイオキシ
ン等の未燃ガス及び未燃カーボンが微量に混在してい
る。これら一酸化炭素又はダイオキシン等の有害物質を
発生させる未燃ガス及び未燃カーボンを含んだ熱気は還
元雰囲気下21中で熱分解し、被焼却物20の上方に漂
うと共に吸引口9cから除去部2aに送り出される。The harmful substances such as carbon monoxide or dioxin are thermally decomposed in a reducing atmosphere and mixed in a trace amount in the hot air containing plenty of smoke escaping above the incinerated material 20. An unburned gas such as carbon monoxide or dioxin and a small amount of unburned carbon are mixed. The unburned gas that generates harmful substances such as carbon monoxide or dioxin and the hot air containing unburned carbon are thermally decomposed in a reducing atmosphere 21, drift above the incinerated material 20, and remove from the suction port 9 c. 2a.
【0052】次に、図11に示すように、酸化燃焼部2
0bは貫通孔9b、9b、9b、9b、9b、・・・よ
り吸入される新鮮な空気が供給されることで、安定した
燃焼を継続する。ところが、前記酸化燃焼部20bの上
の未燃焼部20aには、酸化燃焼部20bを通過するこ
とにより酸素を失うと共に、熱気及び煙を含んだ還元雰
囲気下21が通過するので、前記熱気及び煙を含んだ酸
欠空気により燻燃される燻燃部20cが徐々に形成され
る。Next, as shown in FIG.
Ob is supplied with fresh air sucked from the through holes 9b, 9b, 9b, 9b, 9b,..., Thereby continuing stable combustion. However, the unburned portion 20a above the oxidized combustion portion 20b loses oxygen by passing through the oxidized combustion portion 20b, and also passes through a reducing atmosphere 21 containing hot air and smoke. The smoked part 20c which is smoked by the oxygen-deficient air containing is gradually formed.
【0053】前記酸化燃焼部20b及び燻燃部20cの
範囲は、被焼却物20の内部を通過する空気により、被
焼却物20内の下層から上層へと徐々に酸化燃焼部20
b及び燻燃部20cの範囲を広げていく。The range of the oxidized combustion section 20b and the smoked section 20c is gradually increased from the lower layer to the upper layer in the incinerated material 20 by air passing through the incinerated material 20.
b and the range of the smoked part 20c is expanded.
【0054】更に、図12に示すように、酸化燃焼部2
0bの内部で燃焼し尽くすと、白色の焼却灰部20dが
前記酸化燃焼部20b内に形成される。前記焼却灰20
dは、貫通孔9b、9b、9b、9b、9b、・・・よ
り灰受室8内に設置されている灰受皿7に積もる。Further, as shown in FIG.
When it burns out inside 0b, a white incinerated ash portion 20d is formed in the oxidized combustion portion 20b. The incineration ash 20
d is piled on the ash tray 7 installed in the ash receiving chamber 8 through the through holes 9b, 9b, 9b, 9b, 9b,.
【0055】そして、図13に示すように、被焼却物2
0の燃焼が進むと未燃焼部20a及び薫燃部20cの一
部を突き破るようにして酸化燃焼部20bが上昇する。
この時、被焼却物20の上方から見ると酸化燃焼部20
bが見えるようになる。即ち、図13に示すように、酸
化燃焼部20b及び燻燃部20cが被焼却物20の未燃
焼部20aを徐々に減らしていくと共に、被焼却物20
の下層から順に焼却灰部20dが徐々に大きく形成され
てくる。Then, as shown in FIG.
As the combustion of 0 progresses, the oxidized combustion section 20b rises so as to penetrate a part of the unburned section 20a and the flammable section 20c.
At this time, as viewed from above the incinerated material 20,
b becomes visible. That is, as shown in FIG. 13, the oxidizing and burning part 20 b and the smoking part 20 c gradually reduce the unburned part 20 a of the incinerated material 20, and
The incineration ash portion 20d is gradually increased in order from the lower layer.
【0056】やがて、図14に示すように、未燃焼部2
0a及び燻燃部20cが徐々に燃焼していき未燃焼部2
0a及び燻燃部20cが完全燃焼してしまう。還元雰囲
気が減少して酸化燃焼部20bが大半を占めるようにな
る。この状態では被焼却物20はほぼ完全に燃焼した状
態となり、被焼却物20を上方より見てみると全体が真
っ赤に燃えて大量の熱を発生している。Then, as shown in FIG.
0a and the non-burning part 2c gradually burn.
0a and the smoked part 20c are completely burned. The reducing atmosphere is reduced, and the oxidizing combustion section 20b occupies the majority. In this state, the incinerated material 20 is almost completely burned, and when the incinerated material 20 is viewed from above, the whole is burned red and generates a large amount of heat.
【0057】図15に示すように、被焼却物20が完全
に燃焼し尽きてしまうと、被焼却物20は全て真っ白な
焼却灰のみとなり焼却灰部20dが形成される。そし
て、貫通孔9b、9b、9b、9b、9b、・・・より
灰受室8内の灰受皿7に落下する。As shown in FIG. 15, when the incinerated material 20 is completely burned out, the incinerated material 20 is entirely white incinerated ash, and an incinerated ash portion 20d is formed. Then, the ash falls into the ash tray 7 in the ash receiving chamber 8 through the through holes 9b, 9b, 9b, 9b, 9b,.
【0058】一般に、有害物質をほとんど発生させずに
被焼却物を焼却するには、約800℃以上の高温で燃焼
させることと、燃えかすを残さず完全燃焼させることが
必要であるといわれる。In general, it is said that in order to incinerate the material to be incinerated without generating any harmful substances, it is necessary to burn at a high temperature of about 800 ° C. or more and to burn completely without leaving any cinders.
【0059】本発明である有害物除去焼炉1は、図8及
び図9で示した一次燃焼室9を負圧状態にしてエゼクタ
ー効果により空気を吸い込み万遍なく被焼却物20を燃
焼させる負圧燃焼の方法と、図10から図15に示した
ように、被焼却部の燃焼工程において燃焼及び燻燃を同
時に進行させる半乾留燃焼の方法とにより被焼却物を完
全燃焼させることができるのである。In the harmful substance removing incinerator 1 of the present invention, the primary combustion chamber 9 shown in FIGS. 8 and 9 is brought into a negative pressure state, air is sucked by the ejector effect, and the incinerated matter 20 is evenly burned. As shown in FIGS. 10 to 15, the incineration material can be completely burned by the pressure combustion method and the semi-distillation combustion method in which combustion and smoking are simultaneously advanced in the combustion process of the incineration portion. is there.
【0060】また、吸引口9dより除去部2aに送り込
まれた還元雰囲気は、二次燃焼室11で高温再燃焼さ
れ、前記還元雰囲気に含まれる未燃ガス、未燃カーボ
ン、有機系臭気物、ダイオキシン等が熱分解され完全無
害な燃焼排ガスとして大気中に放出される。The reducing atmosphere sent to the removing section 2a from the suction port 9d is reburned at a high temperature in the secondary combustion chamber 11, and contains unburned gas, unburned carbon, organic odor, and the like contained in the reducing atmosphere. Dioxins and the like are thermally decomposed and released into the atmosphere as completely harmless combustion exhaust gas.
【0061】図16は、本発明である有害物質除去焼却
炉の第4実施例の縦断面図である。本例の有害物質除去
焼却炉では、二次燃焼室11a内の排煙筒11a内にブ
ロワー23の送風管23aの先端部を差し込み設置する
とともに、焼却部2と除去部2aを接続する接続部9e
にバーナ22を設置した構造である。FIG. 16 is a longitudinal sectional view of a fourth embodiment of the incinerator for removing harmful substances according to the present invention. In the incinerator for removing harmful substances of the present example, the tip of the blower tube 23a of the blower 23 is inserted and installed in the flue gas tube 11a in the secondary combustion chamber 11a, and the connecting portion 9e for connecting the incinerator 2 and the removing portion 2a.
This is a structure in which a burner 22 is installed.
【0062】本例の有害物質除去焼却炉では、ブロワー
23からの送風を強制的に排煙筒11a内に送り込み、
排煙筒11aから強制的に煙りを排出させることにより
焼却部2及び除去部2a内を負圧にする方法、即ち、送
風式負圧手段を採用している。In the incinerator for removing harmful substances according to the present embodiment, the blast from the blower 23 is forcibly sent into the smoke stack 11a.
A method of forcibly discharging smoke from the smoke stack 11a to make the inside of the incineration unit 2 and the removal unit 2a negative pressure, that is, a ventilation type negative pressure means is adopted.
【0063】符号6bは、取り込む空気を調節するため
の空気調節弁である。前記空気調節弁6bを炉床6の下
に設け、空気調節弁6bを移動させる方法により炉床6
に形成されている空気取込孔6aを閉じたり開いたりす
ることにより取り込む空気の量を調節するのである。図
1、図2及び図3に示した有害物質除去焼却炉にも、空
気調節弁6bを設けてもよい。Reference numeral 6b is an air control valve for controlling the air taken in. The air control valve 6b is provided below the hearth 6, and the hearth 6 is moved by moving the air control valve 6b.
The amount of air taken in is adjusted by closing or opening the air intake hole 6a formed in the above. The harmful substance removal incinerator shown in FIGS. 1, 2 and 3 may also be provided with the air control valve 6b.
【0064】図17は、本発明である有害物質除去焼却
炉の別の送風式負圧手段(ブロワー式負圧手段)を示し
た縦断面図である。本送風式負圧手段では、符号24は
焼却部や二次燃焼室から排出される煙りを大気中に排出
する排煙部24、符号25はブロワーからの風を排煙部
内24aに送り込むための突出筒、符号26は焼却部、
二次燃焼室に接続する接続部である。FIG. 17 is a longitudinal sectional view showing another blowing type negative pressure means (blower type negative pressure means) of the harmful substance removing incinerator according to the present invention. In this blower type negative pressure means, reference numeral 24 denotes a smoke exhaust unit 24 for discharging smoke discharged from an incineration unit or a secondary combustion chamber into the atmosphere, and reference numeral 25 denotes a blower for blowing air from a blower into a smoke exhaust unit 24a. Projection cylinder, reference numeral 26 is an incineration unit,
It is a connection part connected to the secondary combustion chamber.
【0065】本送風式負圧手段では、ブロワーに接続さ
れている突出筒25の突出筒内25aからブロワーより
強制的に送り込まれる空気は、排煙部24の排煙部内2
4aからを通り強制的に排煙口24bから排出される
が、その時には排煙筒内24aは負圧状態となるため
に、焼却部、二次燃焼室等にある焼却により発生した煙
りが、接続部26の吸引口26aより排煙筒内24a内
に吸引された後、前記煙り(排気ガス)は排煙口24b
から強制的に大気中に排出される。In the blower type negative pressure means, the air forced from the blower from the inside of the projecting cylinder 25a of the projecting cylinder 25 connected to the blower is discharged into the smoke exhaust section 24 of the smoke exhaust section 24.
4a, the gas is forcibly discharged from the smoke exhaust port 24b. At that time, since the inside of the smoke stack 24a is in a negative pressure state, the smoke generated by the incineration in the incineration section, the secondary combustion chamber, etc., is connected. After being sucked from the suction port 26a of the part 26 into the smoke exhaust tube 24a, the smoke (exhaust gas) is discharged to the smoke exhaust port 24b.
Is forcibly released into the atmosphere.
【0066】本発明である有害物質除去焼却炉を示した
図1、図2、図3及び図16では、除去部2aが1基連
設されているように思われるが、前記除去部2aは焼却
部2に複数基設置した構造としてもよい。In FIGS. 1, 2, 3 and 16 showing the incinerator for removing harmful substances according to the present invention, it seems that one removing unit 2a is provided continuously. It is good also as a structure which installed two or more in incineration part 2.
【0067】図18は、本発明である有害物質除去焼却
炉の除去部に代えて取り付けらるサイクロンを示した図
である。図8に示すように、サイクロン27は、下部が
テーパ状に形成されている形状をしている。FIG. 18 is a view showing a cyclone which is attached in place of the removing section of the toxic substance removing incinerator according to the present invention. As shown in FIG. 8, the cyclone 27 has a shape in which a lower portion is formed in a tapered shape.
【0068】前記サイクロン27を除去部2aの代わり
に焼却部2に連設させてもよい。サイクロン内27aに
は、焼却部2内から発生した煙り(排気ガス)が流入す
る。サイクロン内27aに流入した煙り中に含まれる塵
は、塵受け27cに落下し、除塵された煙りは排煙筒2
8内を通り大気中に放出される。The cyclone 27 may be connected to the incineration unit 2 instead of the removal unit 2a. Smoke (exhaust gas) generated from the incineration section 2 flows into the cyclone 27a. The dust contained in the smoke that has flowed into the cyclone 27a falls into the dust catcher 27c, and the removed smoke is discharged to the smoke stack 2
8 to the atmosphere.
【0069】除塵された煙りが、大気中に放出されるの
は、ブロワーの送風管29の先端部から排煙筒28内に
強制的に送出される風に乗り、サイクロン内27aの除
塵された煙りが前記排煙筒28内に吸い込まれて大気中
に放出される。除塵された煙りが強制的放出されると、
サイクロン内27aは負圧となり、焼却部2内の焼却煙
りをサイクロン内27aに吸引するために、前記焼却部
2内も負圧状態となるので、炉床6に形成されている空
気取入孔6aから酸素を含む新鮮な空気が焼却部2内に
取り込まれる。The smoke that has been removed from the dust is released into the atmosphere only when the dust that is forcibly sent out from the end of the blower pipe 29 into the smoke stack 28 is removed from the dust in the cyclone 27a. Is sucked into the smoke stack 28 and released to the atmosphere. When the dedusted smoke is forcibly released,
The inside of the incineration section 2 is also in a negative pressure state in order to suck the incineration smoke in the incineration section 2 into the inside of the cyclone 27a, so that the air intake hole formed in the hearth 6 is formed. Fresh air containing oxygen is taken into the incinerator 2 from 6a.
【0070】[0070]
【発明の効果】本発明は、以上に説明したような構成で
あるから以下の効果が得られる。第1に、一次燃焼室内
の空気量を制御することによって、一次燃焼室内を還元
雰囲気下にし、一酸化炭素、ダイオキシン等の有害物質
の発生を抑制するとともに、下層部は酸化燃焼部で80
0℃以上、上層部は還元雰囲気で300℃以上500℃
で燃焼することによって前記の有害物質を完全に熱分解
し除去することができる。Since the present invention has the above-described configuration, the following effects can be obtained. First, by controlling the amount of air in the primary combustion chamber, the primary combustion chamber is brought into a reducing atmosphere to suppress the generation of harmful substances such as carbon monoxide and dioxin.
0 ° C or higher, upper layer at 300 ° C or higher and 500 ° C in a reducing atmosphere
The above harmful substances can be completely thermally decomposed and removed by burning at the temperature.
【0071】第2に、一次燃焼室では加熱し、排煙を第
二次燃焼室において焼却しすることにより排煙中に含ま
れる有害物質を800℃以上で熱分解し、消煙及び消臭
が効率的になされる。Secondly, the primary combustion chamber is heated, and the flue gas is incinerated in the secondary combustion chamber, whereby harmful substances contained in the flue gas are thermally decomposed at 800 ° C. or more, and smoke and deodorization are performed. Is done efficiently.
【0072】第3に、吸引式負圧手段、送風式負圧手段
等により800℃以上で焼却し、排気ガス(煙り)を前
記手段により送り込んだ空気とを混合し、冷却すると3
00℃以上の排ガスになるために、ダイオキシン等の生
成がなされない。Third, incineration is performed at 800 ° C. or more by a suction type negative pressure means, a ventilation type negative pressure means, etc., and the exhaust gas (smoke) is mixed with the air sent by the above means and cooled.
Since the exhaust gas has a temperature of 00 ° C. or more, dioxin and the like are not generated.
【図1】本発明である有害物質除去焼却炉の第1実施例
の縦断面図である。FIG. 1 is a longitudinal sectional view of a first embodiment of a toxic substance removing incinerator according to the present invention.
【図2】本発明である有害物質除去焼却炉の第2実施例
の縦断面図である。FIG. 2 is a longitudinal sectional view of a second embodiment of the incinerator for removing harmful substances according to the present invention.
【図3】本発明である有害物質除去焼却炉の第3実施例
の縦断面図である。FIG. 3 is a vertical sectional view of a third embodiment of the incinerator for removing harmful substances according to the present invention.
【図4】従来の焼却炉内での空気の流れ方を示した図で
ある。FIG. 4 is a diagram showing a flow of air in a conventional incinerator.
【図5】本発明である有害物質除去焼却炉内での空気の
流れ方を示した図である。FIG. 5 is a diagram showing a flow of air in a toxic substance removing incinerator according to the present invention.
【図6】本発明である有害物質除去焼却炉の焼却部内の
温度の経時変化を示した表である。FIG. 6 is a table showing time-dependent changes in the temperature in the incineration section of the incinerator for removing harmful substances according to the present invention.
【図7】本発明である有害物質除去焼却炉により被焼却
物を焼却した焼却炉の排煙中に含まれるダイオキシンと
ジベンゾフランの濃度と毒性等量濃度を示した表であ
る。FIG. 7 is a table showing the concentrations of dioxins and dibenzofurans and the toxic equivalents contained in flue gas of an incinerator in which incinerators are incinerated by the incinerator for removing harmful substances according to the present invention.
【図8】従来の焼却炉内での空気の流れ方を示した図で
ある。FIG. 8 is a diagram showing a flow of air in a conventional incinerator.
【図9】本発明である有害物質除去焼却炉内での空気の
流れ方を示した図である。FIG. 9 is a view showing a flow of air in a toxic substance removing incinerator according to the present invention.
【図10】本発明である有害物質除去焼却炉の焼却部内
での被焼却物の燃焼状態を示した図である。FIG. 10 is a view showing a combustion state of an incineration object in an incineration section of the harmful substance removing incinerator according to the present invention.
【図11】本発明である有害物質除去焼却炉の焼却部内
での被焼却物の燃焼状態を示した図である。FIG. 11 is a view showing a combustion state of an incineration object in an incineration section of the harmful substance removing incinerator according to the present invention.
【図12】本発明である有害物質除去焼却炉の焼却部内
での被焼却物の燃焼状態を示した図である。FIG. 12 is a view showing a combustion state of an incineration object in an incineration section of the incinerator for removing harmful substances according to the present invention.
【図13】本発明である有害物質除去焼却炉の焼却部内
での被焼却物の燃焼状態を示した図である。FIG. 13 is a view showing a combustion state of an incinerated substance in an incineration section of the incinerator for removing harmful substances according to the present invention.
【図14】本発明である有害物質除去焼却炉の焼却部内
での被焼却物の燃焼状態を示した図である。FIG. 14 is a view showing a combustion state of an incinerated substance in an incineration section of the incinerator for removing harmful substances according to the present invention.
【図15】本発明である有害物質除去焼却炉の焼却部内
での被焼却物の燃焼状態を示した図である。FIG. 15 is a view showing a combustion state of an incineration object in an incineration section of the harmful substance removing incinerator according to the present invention.
【図16】本発明である有害物質除去焼却炉の第4実施
例の縦断面図である。FIG. 16 is a longitudinal sectional view of a fourth embodiment of the incinerator for removing harmful substances according to the present invention.
【図17】本発明である有害物質除去焼却炉の送風式負
圧手段の別の構造を示した縦断面図である。FIG. 17 is a longitudinal sectional view showing another structure of the blast-type negative pressure means of the incinerator for removing harmful substances according to the present invention.
【図18】本発明である有害物質除去焼却炉の除去部の
代わりに取り付けらるサイクロンを示した図である。FIG. 18 is a view showing a cyclone which is attached in place of the removing section of the incinerator for removing harmful substances according to the present invention.
1〜1b 有害物質除去焼却炉 2 焼却部 2a 除去部 3 ファン 3a ブロワー 4 生ゴミ 5 被焼却物 6 炉床 6a 空気取入孔 6b 空気調節弁 7 灰受皿 8 灰受室 9 一次燃焼室 9a 火格子 9b 貫通孔 9c 燃焼室 9d 吸引口 9e 接続部 10 乾燥室 10a 仕切 10b 貫通孔 11 二次燃焼室 11a 排煙筒 12 バーナ 12a 加熱バーナ 13 排煙口 14 ファン 14a 送風 14b 乱流 14c 吸入空気 15 物体(被焼却物) 15a 前面 15b 背面 15c 燃焼部分 15d 未燃焼部分 15e 隙間 16 一次燃焼室出口温度曲線 17 二次燃焼室上部温度曲線 18 450度未満の期間 19 450度以上の期間 20 被焼却物 20a 未燃焼部 20b 酸化燃焼部 20c 燻燃部 20d 焼却灰部 21 還元雰囲気下 22 バーナ 23 ブロワー 24 排煙部 24a 排煙部内 25 突出筒 25a 突出筒内 26 接続部 26a 吸引口 27 サイクロン 27a サイクロン内 27b 下部 27c 塵受け 28 排煙筒 29 送風管 1 to 1b incinerator for removing harmful substances 2 incinerator 2a removing unit 3 fan 3a blower 4 garbage 5 incinerated material 6 hearth 6a air intake hole 6b air control valve 7 ash tray 8 ash receiving chamber 9 primary combustion chamber 9a fire Lattice 9b Through hole 9c Combustion chamber 9d Suction port 9e Connection part 10 Drying chamber 10a Partition 10b Through hole 11 Secondary combustion chamber 11a Smoke stack 12 Burner 12a Heating burner 13 Smoke outlet 14 Fan 14a Blow 14b Turbulence 14c Suction air 15 objects (Incinerated material) 15a Front surface 15b Back surface 15c Burning part 15d Unburned part 15e Gap 16 Primary combustion chamber exit temperature curve 17 Secondary combustion chamber upper temperature curve 18 Period of less than 450 degrees 19 Period of 450 degrees or more 20 Objects to be incinerated 20a Unburned section 20b Oxidized combustion section 20c Smoke section 20d Incinerated ash section 21 Under reducing atmosphere 22 Burner 2 3 Blower 24 Smoke exhaust unit 24a Inside the smoke exhaust unit 25 Projecting cylinder 25a Inside the projecting cylinder 26 Connection 26a Suction port 27 Cyclone 27a Inside the cyclone 27b Lower part 27c Dust pan 28 Smoke exhaust pipe 29 Air blower pipe
Claims (8)
部から発生する有害物質を除去する除去部を連設し、吸
引式負圧手段又は送風式負圧手段により焼却部から除去
部へ空気の流れをつくり、前記焼却部内を常時負圧状態
とすることを特徴とする有害物質除去焼却炉。1. An incineration section for burning incinerators, a removal section for removing harmful substances generated from the incineration section is connected to the incineration section. A harmful substance removal incinerator characterized in that a flow of air is created and the inside of the incineration section is always kept under a negative pressure.
次燃焼室内で被焼却物が焼却され発生する焼却灰を受け
る灰受皿を有する灰受室とからなる焼却部に前記焼却部
から発生する有害物質を除去するバーナが設置されてい
る二次燃焼室と前記二次燃焼室の熱気を吸引し排出する
ためのファンとからなる除去部を連設したことを特徴と
する有害物質除去焼却炉。2. An incineration unit comprising an incineration unit including a primary combustion chamber for burning the incineration material and an ash receiving chamber having an ash tray for receiving incineration ash generated by incineration of the incineration material in the primary combustion chamber. Harmful substance removal and incineration, characterized in that a removal section comprising a secondary combustion chamber in which a burner for removing harmful substances to be removed is installed and a fan for sucking and discharging hot air from the secondary combustion chamber is connected. Furnace.
るための加熱バーナを設けたことを特徴とする請求項2
記載の有害物質除去焼却炉。3. A heating burner for heating an object to be incinerated is provided in a primary combustion chamber of an incineration section.
Hazardous substance removal incinerator as described.
を特徴とする請求項2又は3記載の有害物質除去焼却
炉。4. The incinerator according to claim 2, wherein a drying chamber is provided above the primary combustion chamber.
ナを設けたことを特徴とする請求項2、3又は4記載の
有害物質除去焼却炉。5. The incinerator for removing harmful substances according to claim 2, wherein one or more burners are provided in the secondary combustion chamber of the removing section.
とができようにしたことを特徴とする請求項2、3、4
又は5記載の有害物質除去焼却炉。6. The apparatus according to claim 2, wherein the rotation speed of the fan of the removing unit can be adjusted.
Or the incinerator for removing harmful substances according to 5.
とする請求項1、2、3、4又は5記載の有害物質除去
焼却炉。7. The incinerator for removing harmful substances according to claim 1, wherein the ash tray can be taken in and out.
ーナを備えた二次燃焼室の前記排煙筒の下端中央部の近
接位置に、ブロワーの先端部が位置するように設置した
除去部としたことを特徴とする請求項2、3、4、5、
6又は7記載の有害物質除去焼却炉。8. A removing section in which a removing section is installed such that a tip end of a blower is located at a position near a center of a lower end of the above-mentioned exhaust pipe in a secondary combustion chamber provided with a burner and having a burner therein. Claims 2, 3, 4, 5,
6. The incinerator for removing harmful substances according to 6 or 7.
Priority Applications (16)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP25051898A JP3790979B2 (en) | 1997-09-08 | 1998-09-04 | Toxic substance removal incinerator |
| DE69833204T DE69833204T2 (en) | 1998-09-04 | 1998-09-07 | COMBUSTION PLANT FOR THE REMOVAL OF POLLUTANTS |
| PCT/JP1998/003998 WO2000014450A1 (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| CA002305222A CA2305222C (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| US09/509,941 US6324999B1 (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| IL13592598A IL135925A0 (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing toxic substances |
| NZ504880A NZ504880A (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances with a removal section and where a vacuum is maintained in the burning section |
| BR9815021-9A BR9815021A (en) | 1998-09-04 | 1998-09-07 | Incinerator for removal of toxic substances |
| HK00105347.9A HK1026733B (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| AU89986/98A AU744063B2 (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| KR1020007003899A KR100594699B1 (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| CNB988108429A CN1204359C (en) | 1998-09-04 | 1998-09-07 | Incinerator for removng noxious substances |
| EP98941741A EP1030110B1 (en) | 1998-09-04 | 1998-09-07 | Incinerator for removing noxious substances |
| MYPI99001457A MY122317A (en) | 1998-09-04 | 1999-04-15 | Incinerator for removing noxious substances |
| TW088106785A TW468022B (en) | 1998-09-04 | 1999-04-27 | Incinerator for removing toxic substances |
| IDP990841A ID23126A (en) | 1998-09-04 | 1999-09-03 | THE COMBUSTION PLACE TO TAKE TOXIC MATERIALS |
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP25933897 | 1997-09-08 | ||
| JP9-259338 | 1997-09-08 | ||
| JP25051898A JP3790979B2 (en) | 1997-09-08 | 1998-09-04 | Toxic substance removal incinerator |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH11141835A true JPH11141835A (en) | 1999-05-28 |
| JP3790979B2 JP3790979B2 (en) | 2006-06-28 |
Family
ID=26539800
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP25051898A Expired - Lifetime JP3790979B2 (en) | 1997-09-08 | 1998-09-04 | Toxic substance removal incinerator |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3790979B2 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2013530366A (en) * | 2010-04-23 | 2013-07-25 | レール・リキード−ソシエテ・アノニム・プール・レテュード・エ・レクスプロワタシオン・デ・プロセデ・ジョルジュ・クロード | Fuel combustion furnace and method for controlling combustion in a fuel combustion furnace |
| CN109603457A (en) * | 2018-10-29 | 2019-04-12 | 南通联恒新材料有限公司 | A device for treating dioxins in flue gas |
| CN113587111A (en) * | 2021-08-09 | 2021-11-02 | 绵阳科大久创科技有限公司 | High-temperature incinerator and matched flue gas cooling and purifying tower |
-
1998
- 1998-09-04 JP JP25051898A patent/JP3790979B2/en not_active Expired - Lifetime
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2013530366A (en) * | 2010-04-23 | 2013-07-25 | レール・リキード−ソシエテ・アノニム・プール・レテュード・エ・レクスプロワタシオン・デ・プロセデ・ジョルジュ・クロード | Fuel combustion furnace and method for controlling combustion in a fuel combustion furnace |
| CN109603457A (en) * | 2018-10-29 | 2019-04-12 | 南通联恒新材料有限公司 | A device for treating dioxins in flue gas |
| CN113587111A (en) * | 2021-08-09 | 2021-11-02 | 绵阳科大久创科技有限公司 | High-temperature incinerator and matched flue gas cooling and purifying tower |
| CN113587111B (en) * | 2021-08-09 | 2023-11-24 | 绵阳科大久创科技有限公司 | High-temperature incinerator and matched flue gas cooling and purifying tower |
Also Published As
| Publication number | Publication date |
|---|---|
| JP3790979B2 (en) | 2006-06-28 |
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