JPH03274311A - Incinerating method for gasification of waste plastic and incinerator thereof - Google Patents
Incinerating method for gasification of waste plastic and incinerator thereofInfo
- Publication number
- JPH03274311A JPH03274311A JP7386590A JP7386590A JPH03274311A JP H03274311 A JPH03274311 A JP H03274311A JP 7386590 A JP7386590 A JP 7386590A JP 7386590 A JP7386590 A JP 7386590A JP H03274311 A JPH03274311 A JP H03274311A
- Authority
- JP
- Japan
- Prior art keywords
- secondary combustion
- chamber
- alkali
- combustion chamber
- air
- 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
- 238000002309 gasification Methods 0.000 title claims abstract description 44
- 239000002699 waste material Substances 0.000 title claims abstract description 32
- 239000004033 plastic Substances 0.000 title claims abstract description 24
- 229920003023 plastic Polymers 0.000 title claims abstract description 24
- 238000000034 method Methods 0.000 title claims description 5
- 238000002485 combustion reaction Methods 0.000 claims abstract description 59
- 239000003513 alkali Substances 0.000 claims abstract description 25
- 239000007921 spray Substances 0.000 claims abstract description 19
- 239000003350 kerosene Substances 0.000 claims abstract description 17
- 239000000203 mixture Substances 0.000 claims abstract description 6
- 231100000252 nontoxic Toxicity 0.000 claims abstract description 4
- 230000003000 nontoxic effect Effects 0.000 claims abstract description 4
- 239000007789 gas Substances 0.000 claims description 24
- 239000012530 fluid Substances 0.000 claims description 11
- 238000010574 gas phase reaction Methods 0.000 claims description 3
- 230000003472 neutralizing effect Effects 0.000 claims 1
- 231100000614 poison Toxicity 0.000 claims 1
- 230000007096 poisonous effect Effects 0.000 claims 1
- 238000005507 spraying Methods 0.000 abstract 1
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 18
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 11
- 239000003546 flue gas Substances 0.000 description 11
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 10
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 10
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 7
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 6
- 238000006477 desulfuration reaction Methods 0.000 description 6
- 230000023556 desulfurization Effects 0.000 description 6
- 235000011121 sodium hydroxide Nutrition 0.000 description 6
- 239000011593 sulfur Substances 0.000 description 6
- 229910052717 sulfur Inorganic materials 0.000 description 6
- 230000002378 acidificating effect Effects 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 3
- 239000000460 chlorine Substances 0.000 description 3
- 229910052801 chlorine Inorganic materials 0.000 description 3
- 238000009434 installation Methods 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- 238000012423 maintenance Methods 0.000 description 3
- -1 polypropylene Polymers 0.000 description 3
- 239000011819 refractory material Substances 0.000 description 3
- 230000000630 rising effect Effects 0.000 description 3
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical compound S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 3
- 239000010920 waste tyre Substances 0.000 description 3
- 208000030507 AIDS Diseases 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 239000004809 Teflon Substances 0.000 description 2
- 229920006362 Teflon® Polymers 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 208000015181 infectious disease Diseases 0.000 description 2
- 239000002906 medical waste Substances 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000004071 soot Substances 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- 206010011224 Cough Diseases 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- JOYRKODLDBILNP-UHFFFAOYSA-N Ethyl urethane Chemical compound CCOC(N)=O JOYRKODLDBILNP-UHFFFAOYSA-N 0.000 description 1
- 229920002430 Fibre-reinforced plastic Polymers 0.000 description 1
- 244000043261 Hevea brasiliensis Species 0.000 description 1
- 239000004677 Nylon Substances 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- IDCBOTIENDVCBQ-UHFFFAOYSA-N TEPP Chemical compound CCOP(=O)(OCC)OP(=O)(OCC)OCC IDCBOTIENDVCBQ-UHFFFAOYSA-N 0.000 description 1
- 229920001807 Urea-formaldehyde Polymers 0.000 description 1
- BZHJMEDXRYGGRV-UHFFFAOYSA-N Vinyl chloride Chemical compound ClC=C BZHJMEDXRYGGRV-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000011151 fibre-reinforced plastic Substances 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 229920003052 natural elastomer Polymers 0.000 description 1
- 229920001194 natural rubber Polymers 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 229920001778 nylon Polymers 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 239000004800 polyvinyl chloride Substances 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 235000011888 snacks Nutrition 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 229920003051 synthetic elastomer Polymers 0.000 description 1
- 239000005061 synthetic rubber Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
Abstract
Description
【発明の詳細な説明】
「産業上の利用分野」
本発明はP、P、(ポリプロピレン)、P、E、(ポリ
エチレン)、発泡ウレタン、ナイロン、テトロン(商品
名)、テフロン(商品名)、P。Detailed Description of the Invention "Field of Industrial Application" The present invention is applicable to P, P, (polypropylene), P, E, (polyethylene), urethane foam, nylon, Tetron (trade name), Teflon (trade name), P.
V、C,(ポリ塩化ビニール) 、F、R,P、(繊維
強化プラスチック)、ユリア樹脂、テフロン以外のフッ
素樹脂、合成ゴムと天然ゴムから成る廃タイヤ等の廃棄
プラスチックを一旦可燃ガス化して完全燃焼し、大がか
りな排煙脱硝装置や排煙脱流装置の必要のない簡易な廃
棄プラスチックのガス化焼却方法およびその焼却炉に関
するものである。V, C, (polyvinyl chloride), F, R, P, (fiber reinforced plastic), urea resin, fluororesins other than Teflon, waste tires and other waste plastics made of synthetic rubber and natural rubber are turned into flammable gas. The present invention relates to a simple gasification and incineration method for waste plastics that is completely combusted and does not require large-scale flue gas denitrification equipment or flue gas deflow equipment, and an incinerator therefor.
「従来の技術」
従来、この種廃棄プラスチックは通常の焼却炉で焼却し
ていたが、環境汚染が社会問題化するに従って大がかり
な排煙脱硝装置や排煙脱硫装置を付設した焼却炉を使用
し°C焼却されている。``Conventional technology'' Previously, this type of waste plastic was incinerated in a normal incinerator, but as environmental pollution became a social issue, incinerators equipped with large-scale flue gas denitrification equipment and flue gas desulfurization equipment were used. °C incinerated.
「発明が解決しようとする課題」
従来の大がかりな排煙脱硝装置や排煙脱硫装置等の設備
を付設した焼却炉は設置スペースを広く要し、焼却炉自
体の設備費や維持費が高価に付き、一般の会社等では設
置できず、自社等でIJI−出する廃棄プラスチックは
産業廃棄物として処理業者に依頼し、前記設備を備えた
焼却炉で焼却処理等を行わねばならず、それにはコスト
も嵩むという大なる欠点を存したものである。"Problem to be solved by the invention" Conventional incinerators equipped with equipment such as large-scale flue gas denitrification equipment and flue gas desulfurization equipment require a large amount of installation space, and the equipment and maintenance costs of the incinerator itself are expensive. Therefore, general companies cannot install IJI, and the waste plastics generated by their own companies must be treated as industrial waste by a processing company and incinerated in an incinerator equipped with the above equipment. This has the major drawback of increasing costs.
また病院等で排出される射注器等の医療廃棄物は前記焼
却炉への移送途中で、エイズ等の感染のおそれがある等
の危険性を存したものである。In addition, medical waste such as syringes and the like discharged at hospitals and the like poses a risk of infection such as AIDS during the transfer to the incinerator.
本発明は大がかりな排煙脱硝装置や排煙脱硫装置等の設
備を必要とせず、排煙脱硝および脱硫機能を有し、設置
スペースも狭くてよく、焼却炉自体の設備費や維持費が
安価で、一般の会社や病院等でも設置可能な簡易な廃棄
プラスチックのガス化焼却方法およびその焼却炉を提供
することを目的とする。The present invention does not require equipment such as large-scale flue gas denitrification equipment or flue gas desulfurization equipment, has flue gas denitrification and desulfurization functions, requires only a small installation space, and has low equipment and maintenance costs for the incinerator itself. The purpose of the present invention is to provide a simple gasification and incineration method for waste plastics that can be installed in general companies, hospitals, etc., and an incinerator for the same.
「課題を解決するための手段J
前記目的を達成するために、本発明は廃棄プラスチック
に着火バーナーで点火し、微風を供給しながら2〜8時
間の長時間をかけて燃焼させ、可燃ガスを発生ずる密封
状一次ガス化室を設け、該一次ガス化仝からの可燃ガス
を一次ガス化室に通路を介して連結した二次燃焼室へ、
該通路に設備したジェットポンプにより一次ガス化室を
負圧にしながら、二次燃焼空気と共に供給し、二次燃焼
室にスプレーノズルと二次バーナーとを設備し、該ノズ
ルとバーナーに灯油とアルカリの混合物または該混合物
とノズルには別途アルカリを供給するようにし、ジェッ
トポンプの第一流体入口よりの圧縮空気と第二流体入口
よりの二次燃焼空気とで二次燃焼室に充分な燃焼用酸素
量を送り込み、同時にジェットポンプで発生ずる真空圧
を利用して一次ガス化室で発生した可燃ガスを送り込み
、該二次燃焼室で二次バーナーにより該可燃ガスを完全
燃焼させると共に、可燃ガスφの酸性ガス、NOX、
so2等の有害ガス、有毒ガスとアルカリ、水等とに気
相反応を起こさせ、中和、吸収して無害化、無毒化する
ようにしたものである。Means for Solving the Problems J In order to achieve the above object, the present invention ignites waste plastic with an ignition burner, burns it for a long time of 2 to 8 hours while supplying a breeze, and generates combustible gas. a sealed primary gasification chamber in which gas is generated, and the combustible gas from the primary gasification chamber is transferred to a secondary combustion chamber connected to the primary gasification chamber via a passage;
A jet pump installed in the passage makes the primary gasification chamber negative pressure and supplies it together with secondary combustion air.The secondary combustion chamber is equipped with a spray nozzle and a secondary burner, and the nozzle and burner are filled with kerosene and alkali. or the mixture and the nozzle are separately supplied with alkali, and the compressed air from the first fluid inlet of the jet pump and the secondary combustion air from the second fluid inlet are used to provide sufficient combustion in the secondary combustion chamber. At the same time, the combustible gas generated in the primary gasification chamber is sent in using the vacuum pressure generated by the jet pump, and the combustible gas is completely combusted by the secondary burner in the secondary combustion chamber, and the combustible gas is φ acid gas, NOX,
It causes a gas phase reaction between harmful gases such as SO2, toxic gases, and alkalis, water, etc., and neutralizes and absorbs them to render them harmless and non-toxic.
「作用」
本発明は廃棄プラスチックを密封状一次ガス化室1で微
風を供給しながら燃焼し゛C可燃ガス化し、エアーコン
プレッサー5からの圧縮空気によりファン19からの二
次燃焼空気を加速するジェットポンプ17の真空力を利
用して該圧縮空気と加速された二次燃焼空気と共に該可
燃ガスを二次燃焼室14に送り込み、二次バーナー24
により灯油を燃焼させて完全燃焼させるから、煤、灰分
、粉塵の発生が殆どなく、煤煙の発生を防止できる。"Function" The present invention burns waste plastic in a sealed primary gasification chamber 1 while supplying a breeze to turn it into combustible gas, and uses compressed air from an air compressor 5 to accelerate secondary combustion air from a fan 19 using a jet pump. The combustible gas is sent into the secondary combustion chamber 14 along with the compressed air and the accelerated secondary combustion air using the vacuum force of the secondary burner 24.
Since the kerosene is completely combusted, there is almost no generation of soot, ash, or dust, and the generation of soot and smoke can be prevented.
また廃棄プラスチ・ツク中に塩素(CI)が含有されて
いる場合、塩素ガス(CtZ)となって一次ガス化室1
内あるいは二次燃焼室14内の水(U2O)と反応し、
次式により塩酸ガス(HCI)として二次燃焼室14内
に送り込まれたり、二次燃焼室14内で生成される。In addition, if the waste plastic contains chlorine (CI), it becomes chlorine gas (CtZ) and enters the primary gasification chamber 1.
Reacts with water (U2O) inside or in the secondary combustion chamber 14,
Hydrochloric acid gas (HCI) is sent into the secondary combustion chamber 14 or generated within the secondary combustion chamber 14 according to the following equation.
2Ch +2JO→2HC1十〇□
この酸性ガスとしての塩酸は二次燃焼室14内にスプレ
ーノズル23および二次バーナー24により供給される
アルカリ (例えばカセイソーダ)と反応して次式によ
り中和されて無害化される。2Ch +2JO→2HC110□ This acidic hydrochloric acid reacts with the alkali (for example, caustic soda) supplied into the secondary combustion chamber 14 by the spray nozzle 23 and the secondary burner 24, and is neutralized by the following formula and becomes harmless. be converted into
HCI +NaOH−+ NaC1+l(g。HCI + NaOH- + NaCl + l (g.
また廃タイヤ等に含まれるS(イオウ)は一次ガス化室
1で燃焼され、次式により有毒なイオウ酸化物(SO,
)となり、一部は二次燃焼室14内に送り込まれる。In addition, S (sulfur) contained in waste tires, etc. is burned in the primary gasification chamber 1, and is converted into toxic sulfur oxide (SO,
), and a portion is sent into the secondary combustion chamber 14.
S十〇t→S02
咳イオウ酸化物は一部ガス化室1および二次燃焼室14
内で水との接触で次式により硫酸とイオウを生しる。S10t→S02 Cough sulfur oxides are partially transferred to the gasification chamber 1 and secondary combustion chamber 14
When it comes in contact with water, it produces sulfuric acid and sulfur according to the following formula.
3SOt +2H!0− HtS!Oa +It!SO
4Hg5zO1→S +HzSO<
ここで上式のイオウは一次ガス化室l、二次燃焼室14
内で再び燃焼され、上式のように硫酸とイオウを生しる
もので、二次燃焼室14内には硫酸とごく微量のイオウ
酸化物とイオウが存在することになり、酸性ガスとして
の硫酸は前記同様に次式によりカセイソーダと反応して
中和され、無毒化され、顕著な脱硫効果が達成される。3SOt +2H! 0-HtS! Oa+It! S.O.
4Hg5zO1→S +HzSO< Here, the sulfur in the above equation is the primary gasification chamber l, the secondary combustion chamber 14
As shown in the above equation, sulfuric acid and sulfur are produced again in the secondary combustion chamber 14, and sulfuric acid and a very small amount of sulfur oxide and sulfur are present in the secondary combustion chamber 14. As described above, sulfuric acid is neutralized and detoxified by reacting with caustic soda according to the following formula, and a remarkable desulfurization effect is achieved.
142SO4+2NaOH−+NazSO1+2HzO
さらに窒素(N)を含有した廃棄プラスチックが燃焼す
ることによって生じる窒素酸化物(No、)は二次燃焼
室14内にスプレーノズル23と二次バーナー24とに
より噴霧、噴射して供給されるアルカリが吸収液となり
吸収除去されるものである。142SO4+2NaOH-+NazSO1+2HzO
Furthermore, nitrogen oxides (No.) produced by the combustion of waste plastics containing nitrogen (N) are atomized and injected into the secondary combustion chamber 14 by a spray nozzle 23 and a secondary burner 24 to supply an alkali. becomes an absorbing liquid and is absorbed and removed.
「実施例」
今、ここに本発明実施の一例を示す概略機構図について
詳説する。"Example" Now, a schematic mechanical diagram showing an example of implementing the present invention will be explained in detail.
lは一部ガス化室で、内壁に耐火物をライニングしたス
テンレスfjl板または鉄板で周囲を囲繞して上下およ
び側壁を構威し、密封性を持たせたもので、前方側壁か
ら土壁にかけて廃棄物投入口2を開口し、開閉自在に該
投入口2を密閉する廃棄物投入扉2aを設備したもので
ある。L is a part of the gasification chamber, and the inner wall is surrounded by stainless FJL plates or iron plates lined with refractories to form the top, bottom, and side walls to provide airtightness, and from the front side wall to the earthen wall. A waste inlet door 2a is provided which opens the waste inlet 2 and closes the inlet 2 in a freely openable and closable manner.
3は一次ガス化室lの下壁、中間および下方の側壁に穿
設した複数の空気供給孔で、下壁に穿設した該空気供給
孔3の一部にエアーパイプ4により弁4aを介してエア
ーコンプレッサー5と連結し、残りの下壁および下方側
壁の空気供給孔3にエアバイブロにより手動弁8を介し
て低圧ブロア(ターボブロア)7と連結し、それぞれエ
アーコンプレッサー5よりの圧縮空気と低圧ブロア7よ
りの微風を供給し、中間側壁の空気供給孔3には一部ガ
ス化室1の中間部側壁外周面に配置したダクト9に該エ
アーパイプロの分岐バイブロaと弁6bを介して連結し
、低圧ブロア7よりの微風を供給するものである。10
は一部ガス化室1の下方側壁に設備した着火バーナーで
、LPGボンベ11と弁12aを介してガスパイプ12
により連結し、点火後において弁12aを閉じると、一
次ガス化室lに着火バーナー10を介しての空気の流入
を防止するものである。I3は前記一次ガス化室1の前
下方側壁に開口した下部投入兼灰取出口で、開閉自在に
下部投入兼灰取出口扉13aを設備し、廃タイヤ等の大
形の廃棄物を投入する際や、一次ガス化室lで燃焼後の
灰を取出す時に該扉13aを開扉して開口し、一次ガス
化室lの燃焼時には閉扉して該取出口13を密閉するも
のである。Reference numeral 3 denotes a plurality of air supply holes drilled in the lower wall, intermediate and lower side walls of the primary gasification chamber l, and an air pipe 4 is connected to a part of the air supply hole 3 bored in the lower wall through a valve 4a. The remaining lower wall and lower side wall air supply holes 3 are connected to a low pressure blower (turbo blower) 7 via a manual valve 8 by an air vibro, and the compressed air from the air compressor 5 and the low pressure blower are connected to the air supply hole 3 of the remaining lower wall and lower side wall. A part of the air supply hole 3 in the intermediate side wall is connected to a duct 9 disposed on the outer peripheral surface of the intermediate side wall of the gasification chamber 1 via a branch vibro a of the air pipe and a valve 6b. A breeze is supplied from the low pressure blower 7. 10
is an ignition burner partially installed on the lower side wall of the gasification chamber 1, which connects the gas pipe 12 through the LPG cylinder 11 and the valve 12a.
When the valve 12a is closed after ignition, air is prevented from flowing into the primary gasification chamber l via the ignition burner 10. I3 is a lower input/ash removal port opened in the lower front side wall of the primary gasification chamber 1, and is equipped with a lower input/ash removal door 13a that can be opened and closed to input large waste such as scrap tires. The door 13a is opened to take out the ash after combustion in the primary gasification chamber 1, and the door 13a is closed to seal the outlet 13 when the primary gasification chamber 1 is incinerated.
14は一部ガス化室1の後上方に設備した前後両面を閉
塞した円筒形状または角筒形状の二次燃焼室で、該ガス
化室1と同様に内壁に耐火物をライニングしたステンレ
ス鋼板または鉄板で円形または角形の前後両面および筒
状側面を囲繞して密閉性を持たせたものである。15は
一次ガス化室1の土壁と二次燃焼室14の前壁中心部を
貫通して連通ずる通路で、二次燃焼室14の中心部通路
15aと一次ガス化室lよりの立ち上がり通路15bと
から成り、内壁に耐火物をライニングしたステンレス鋼
板または鉄板で周囲を囲繞して密閉性を有する側壁16
を設けて構成したものである。17はジェットポンプで
、二次燃焼室14の前壁と対峙する中心部通路15aの
側壁16に、前記立ち上がり通路15bに先端が達しな
いように設備したもので、駆動用第一流体入口17aを
前記エアーコンプレッサー5とエアーパイプ18により
弁18aを介して連結し、第2流体人ロ17bを二次燃
焼空気供給用ターボファン19と弁20aを介してエア
ーパイプ20で連結したものである。21は該側壁16
の中心部通路15aの二次燃焼室14側に設けた該燃焼
室14側が拡大したテーパ孔である。22は排気筒で、
二次燃焼室14の通路15aのテーパ孔21から隔たっ
た後壁寄りの筒状側面の上面に開口したもので、該排気
筒22西に温度センサーTICを設備し、二次燃焼室1
4内が700〜800°C以下に下がると、TICによ
り公知のように後述のバーナー24を自動着火し、灯油
を燃焼するようにしてもよいものである。23はスプレ
ーノズルで、IJL気筒22から隔たった、該テーパ孔
21と近接した二次燃焼室14の前壁と筒状側面との接
合上隅部に設備したものであり、24は二次バーナーで
、該スプレーノズル23と同様に二次燃焼室14の前壁
と筒状側面との接合下隅部に設けたもので、それぞれオ
イルパイプ25.26と連結し、該オイルパイプ25.
26の基端を弁25a、26aを介して合岐してオイル
バイブ27に連結し、カセイソーダ(NaOH)等のア
ルカリを混入した灯油タンク28とオイルポンプ29を
介して連結し、灯油タンク28内の灯油とアルカリとの
混合物をスプレーノズル23により二次燃焼室14内に
噴霧、噴射すると同時に、二次バーナー24により灯油
を勢いよく燃焼させると共にアルカリを噴霧、噴射する
ものである。30はカセイソーダ等のアルカリ専用タン
クで、該タンク30とスプレーノズル23に連結したオ
イルバイブ25とを順次アルカリポンプ31と弁32a
を介してバイブ32により連結し、塩化ビニール等の酸
性ガスの発生の多い廃棄プラスチックを焼却する場合に
、弁32aを開き、アルカリポンプ31により多量のア
ルカリをスプレーノズル23から噴霧、噴射するように
したものである。14 is a cylindrical or prismatic secondary combustion chamber partially installed at the rear and upper part of the gasification chamber 1 with both front and rear sides closed, and like the gasification chamber 1, the inner wall is made of stainless steel plate or lining with refractory material. The front and rear sides of a circular or square shape, as well as the cylindrical side surface, are surrounded by iron plates to provide airtightness. Reference numeral 15 denotes a passage that passes through and communicates with the earthen wall of the primary gasification chamber 1 and the center of the front wall of the secondary combustion chamber 14, and is connected to the central passage 15a of the secondary combustion chamber 14 and the passage rising from the primary gasification chamber l. 15b, and the inner wall is surrounded by a stainless steel plate or iron plate lined with refractory material to provide airtightness.
It is configured by providing. A jet pump 17 is installed on the side wall 16 of the central passage 15a facing the front wall of the secondary combustion chamber 14 so that its tip does not reach the rising passage 15b, and has a first driving fluid inlet 17a. The air compressor 5 and the air pipe 18 are connected through a valve 18a, and the second fluid manifold 17b is connected to the secondary combustion air supply turbo fan 19 through a valve 20a through an air pipe 20. 21 is the side wall 16
This is a tapered hole provided on the secondary combustion chamber 14 side of the central passage 15a of which is enlarged on the combustion chamber 14 side. 22 is the exhaust pipe,
It opens on the upper surface of the cylindrical side surface near the rear wall separated from the tapered hole 21 of the passage 15a of the secondary combustion chamber 14, and a temperature sensor TIC is installed on the west side of the exhaust pipe 22.
When the temperature inside the burner 4 drops below 700 to 800°C, the TIC may automatically ignite the burner 24, which will be described later, to burn kerosene, as is well known. 23 is a spray nozzle, which is installed at the upper corner of the junction between the front wall and the cylindrical side surface of the secondary combustion chamber 14, which is separated from the IJL cylinder 22 and close to the tapered hole 21; Like the spray nozzle 23, it is provided at the lower corner of the junction between the front wall and the cylindrical side surface of the secondary combustion chamber 14, and is connected to the oil pipes 25 and 26, respectively.
The proximal ends of 26 are connected to an oil vibe 27 via valves 25a and 26a, and are connected to a kerosene tank 28 containing an alkali such as caustic soda (NaOH) via an oil pump 29. A mixture of kerosene and alkali is atomized and injected into the secondary combustion chamber 14 by the spray nozzle 23, and at the same time, the kerosene is vigorously burned by the secondary burner 24 and the alkali is atomized and injected. 30 is a tank exclusively for alkali such as caustic soda, and the tank 30 and the oil vibe 25 connected to the spray nozzle 23 are sequentially connected to the alkali pump 31 and the valve 32a.
When incinerating waste plastics such as vinyl chloride that generate a large amount of acidic gas, the valve 32a is opened and the alkali pump 31 atomizes and injects a large amount of alkali from the spray nozzle 23. This is what I did.
これを使用するに当たっては、廃棄物投入扉2aあるい
は下部投入無灰取出口扉13aを開扉し、一次ガス化室
l内に前記廃棄プラスチックを投入し、該投入]ff2
aあるいは投入兼灰取出口扉13aを密封し、着火バー
ナーlOで廃棄プラスチックに点火し、弁12aを閉し
て着火ノ\−ナーlOよりの空気の流入を防止し、エア
ーパイプ46および分岐バイブロaのそれぞれ弁4a、
手動弁8および弁6bを介してエアーコンプレッサー5
の圧縮空気および低圧プロ′77の微風を供給し、2〜
8時間の長時間かけての燃焼を開始すると同時に弁18
aを開け、エアーコンプレッサー5よりの圧縮空気を駆
動用流体としてジェットポンプ17の第1流体人ロ17
aにイ」(給すると、弁20aを開けて二次燃焼空気供
給用ターボファン19よりエアーパイプ20を介し゛C
第2流体人ロ17bに供給される二次燃焼空気は高スピ
ードとなり、側壁16の二次燃焼室14の中心部通路1
5aからテーパ孔21を介して二次燃焼室14山に吹き
込まれる。このとき一次ガス化室lの上面から該中心部
通路15aに至る立ち上がり通路15bが真空となり、
一次ガス化室lを負圧として該ガス化室lで発生した可
燃ガス、酸性ガス、NO,等は二次燃焼空気のジェット
流と共に二次燃焼室14内に吹き込まれる。To use this, open the waste input door 2a or the lower input ashless outlet door 13a, and input the waste plastic into the primary gasification chamber l.
Alternatively, seal the input/ash removal exit door 13a, ignite the waste plastic with the ignition burner lO, close the valve 12a to prevent air from flowing in from the ignition nozzle lO, and close the air pipe 46 and branch vibro. each valve 4a of a;
Air compressor 5 via manual valve 8 and valve 6b
of compressed air and a breeze of low pressure pro'77,
At the same time as starting combustion over a long period of 8 hours, valve 18
a, and use the compressed air from the air compressor 5 as the driving fluid to operate the jet pump 17 in the first fluid chamber 17.
When the air is supplied to a, the valve 20a is opened and the secondary combustion air is supplied from the turbo fan 19 through the air pipe 20.
The secondary combustion air supplied to the second fluid chamber 17b has a high speed, and the central passage 1 of the secondary combustion chamber 14 in the side wall 16
It is blown into the secondary combustion chamber 14 from 5a through the tapered hole 21. At this time, the rising passage 15b from the upper surface of the primary gasification chamber l to the central passage 15a becomes vacuum,
The primary gasification chamber 1 is made to have a negative pressure, and combustible gas, acidic gas, NO, etc. generated in the gasification chamber 1 are blown into the secondary combustion chamber 14 together with a jet stream of secondary combustion air.
その内、該二次燃焼室14内に吹き込まれた可燃ガスは
エアーパイプ18を介し′Cのエアーコンプレッサー5
からの圧縮空気とターボファン19よりのエアーパイプ
20を介しての二次燃焼空気とから充分な燃焼用酸素量
を与えられ、スフ’ L/−ノズル23により噴霧、噴
射された灯油と共に二次バーナー24からの灯油の炎に
より点火され完全燃焼するものである。The combustible gas blown into the secondary combustion chamber 14 is passed through the air pipe 18 to the air compressor 5 'C.
A sufficient amount of combustion oxygen is provided from the compressed air from the turbo fan 19 and the secondary combustion air from the air pipe 20, and the secondary combustion air is supplied with kerosene which is atomized and injected by the SFU' L/- nozzle 23. It is ignited by the kerosene flame from the burner 24 and completely burns.
また廃棄プラスチック中の塩素やイオウ等と水との接触
により生しる塩酸、硫酸等の酸性ガスはスプレーノズル
23、二次バーナー24から噴霧、噴射される灯油タン
ク28およびアルカリ専用タンク30からのアルカリ
(NaOH等)と気相反応して中和され、無害あるいは
無毒の塩となるものである。In addition, acidic gases such as hydrochloric acid and sulfuric acid produced when chlorine, sulfur, etc. in waste plastic come into contact with water are sprayed and injected from the spray nozzle 23 and the secondary burner 24, and from the kerosene tank 28 and the alkali tank 30. alkali
It is neutralized by a gas phase reaction with (NaOH etc.) and becomes a harmless or non-toxic salt.
さらに窒素酸化物(NOX)は前記スプレーノズル23
およびバーナー24から噴霧、噴射されるアルカリ(N
aOH等)に吸収され除去される。Furthermore, nitrogen oxides (NOX) are removed from the spray nozzle 23.
and alkali (N) sprayed from the burner 24.
aOH etc.) and removed.
「発明の効果」
本発明は以上のような構成で、排煙脱硝および排煙脱硫
のために大がかりな専用装置も必要なく、一次ガス化室
1と二次燃焼室14とだけで構成されるため、構成が簡
単となって設備費および維持費が安価であり、故障も少
なく、設置スペースも少くてずみ、−船会社や病院等で
も既設の焼却炉に代えて設置が可能で、自社等で排出す
る廃棄プラスチックを公害発生のおそれなく、安全に処
理することができ、廃棄プラスナックの処理費用を大幅
に削減することが可能である。"Effects of the Invention" With the above configuration, the present invention does not require any large-scale dedicated equipment for flue gas denitrification and flue gas desulfurization, and is comprised only of the primary gasification chamber 1 and the secondary combustion chamber 14. Therefore, the configuration is simple, equipment costs and maintenance costs are low, there are few breakdowns, and the installation space is small. It is possible to safely dispose of waste plastics emitted by plants without the risk of causing pollution, and it is possible to significantly reduce the cost of processing waste plastic snacks.
また病院等で発生ずる医療廃棄物は各病院等で焼却処理
でき、エイズ等の感染のおそれもなく、安全に処理が可
能となる。In addition, medical waste generated at hospitals can be incinerated at each hospital, making it possible to safely dispose of it without fear of infection with AIDS or the like.
添付図面は本発明実施の一例を示したものであり、本発
明の焼却炉の一部断面とした概略機構図である。
l−・−−一次ガス化室、2・・−廃棄物投入口、2a
・・廃棄物投入扉、3・・・空気供給孔、4−エアーパ
イプ、4a・・・弁、5−エアーコンプレッサー6・・
・エアーパイプ、6a・・・分岐パイプ、6a−“弁、
7・−・低圧ブロア、8−手動弁、9・・・ダクト、1
0−一゛着火バーナー 11・−・LPGボンベ、12
ガスパイプ、12a・・−弁、13−・下部投入兼灰取
出口、13a−下部投入無灰取出口扉、14二次燃焼室
、15−通路、15a−中心部通路、15 b−立ち上
がり通路、16−・側壁、17ジエツトポンプ、l 7
a−駆動用第1流体入口、17b・−第二流体入口、
18−エアーパイプ、18a・・−弁、19−二次燃焼
空気供給用ターボファン、2o・・−エアーパイプ、2
0a−弁、21−・−テーバ孔、22−排気筒、23−
スプレーノズル、24・・−二次バーナー 25.26
オイルパイプ、25a、26a−弁、27−オイルパイ
プ、28−灯油タンク、29・−オイルポンプ、30・
・−アルカリ専用タンク、31−アルカリポンプ、32
−・パイプ、32a−弁。The accompanying drawings show an example of the implementation of the present invention, and are schematic diagrams of the incinerator of the present invention, partially in cross section. l---Primary gasification chamber, 2...-Waste inlet, 2a
...Waste input door, 3...Air supply hole, 4-Air pipe, 4a...Valve, 5-Air compressor 6...
・Air pipe, 6a...branch pipe, 6a-"valve,
7--Low pressure blower, 8-Manual valve, 9-Duct, 1
0-1゛Ignition burner 11...LPG cylinder, 12
Gas pipe, 12a...-valve, 13--lower input and ash removal outlet, 13a-lower input ashless outlet door, 14 secondary combustion chamber, 15-passage, 15a-center passage, 15b-rising passageway, 16-・Side wall, 17 Jet pump, l 7
a - first fluid inlet for driving; 17b - second fluid inlet;
18-air pipe, 18a...-valve, 19-secondary combustion air supply turbo fan, 2o...-air pipe, 2
0a-valve, 21--Taber hole, 22-exhaust pipe, 23-
Spray nozzle, 24...-Secondary burner 25.26
Oil pipe, 25a, 26a-valve, 27-oil pipe, 28-kerosene tank, 29--oil pump, 30-
・-Alkali tank, 31-Alkali pump, 32
-・Pipe, 32a-valve.
Claims (1)
供給しながら2〜8時間かけて燃焼させる密封状一次ガ
ス化室からの可燃ガスを、ジェットポンプにより二次燃
焼空気を吹き入むと同時に、該一次ガス化室を負圧とし
て二次燃焼室に供給し、二次燃焼室にスプレーノズルお
よび二次バーナーにより灯油とアルカリの混合物を噴霧
、噴射して該二次燃焼室で完全燃焼させると共に、前記
ガス中の有害ガス、有毒ガスと気相反応を起こさせ、中
和、吸収して無害化、無毒化することを特徴とする廃棄
プラスチックのガス化焼却方法。 2、スプレーノズルおよび二次バーナーからの灯油とア
ルカリの混合物の外に、スプレーノズルよりアルカリを
噴霧、噴射することを特徴とする請求項1記載の廃棄プ
ラスチックのガス化焼却方法。 3、廃棄物投入口を上側方に開口し、該投入口を密閉す
る廃棄物投入扉を開閉自在に設備し、下面、中間および
下方側面に複数の空気供給孔を穿設し、該供給孔のそれ
ぞれにエアーコンプレッサーおよび低圧ブロアーと連結
したエアーパイプを配管した密封状一次ガス化室を設け
、該ガス化室の下方側面に点火後に該ガス化室への空気
の流入を防止する着火バーナーを設備し、該ガス化室の
上方に二次燃焼室を設備し、該ガス化室の上方と二次燃
焼室の側方とを連通する通路を設け、一次ガス化室と二
次燃焼室とを連結し、該通路部にジェットポンプを設備
し、該ジェットポンプの駆動用第一流体入口と前記エア
ーコンプレッサーとをエアーパイプを介在して連結し、
該ジェットポンプの第二流体入口に二次燃焼空気供給用
ファンを連結し、二次燃焼室上方に排気孔を開口し、該
排気孔と隔って二次燃焼室の上方にスプレーノズルと下
方に二次バーナーとを設備し、該スプレーノズルと二次
バーナーとにポンプを介して灯油とアルカリの混合タン
クを連結し、スプレーノズルから灯油とアルカリを噴霧
、噴射し、二次バーナーにより前記ガス化室からのガス
を燃焼させることを特徴とする廃棄プラスックのガス化
焼却炉。 4、灯油とアルカリの混合タンクとスプレーノズルとの
間にアルカリ専用タンクをポンプを介して連結したこと
を特徴とする請求項3記載の廃棄プラスチックのガス化
焼却炉。[Claims] 1. Combustible gas from a sealed primary gasification chamber where waste plastic is ignited with an ignition burner and burned for 2 to 8 hours while supplying a breeze, and secondary combustion air is supplied using a jet pump. At the same time, the primary gasification chamber is turned into a negative pressure and supplied to the secondary combustion chamber, and a mixture of kerosene and alkali is sprayed and injected into the secondary combustion chamber by a spray nozzle and a secondary burner. A method for gasification and incineration of waste plastics, characterized in that the waste plastics are completely combusted, and the waste plastics are made harmless and non-toxic by causing a gas phase reaction with harmful gases and poisonous gases in the gas, and neutralizing and absorbing them. 2. The method for gasifying and incinerating waste plastics according to claim 1, characterized in that the alkali is sprayed and injected from the spray nozzle in addition to the mixture of kerosene and alkali from the spray nozzle and the secondary burner. 3. A waste inlet is opened to the upper side, a waste inlet door that seals the inlet is openable and closable, and a plurality of air supply holes are bored in the bottom, middle, and lower side. Each is provided with a sealed primary gasification chamber equipped with an air pipe connected to an air compressor and a low-pressure blower, and an ignition burner is installed on the lower side of the gasification chamber to prevent air from flowing into the gasification chamber after ignition. A secondary combustion chamber is installed above the gasification chamber, a passage is provided that communicates the upper side of the gasification chamber with the side of the secondary combustion chamber, and the primary gasification chamber and the secondary combustion chamber are connected to each other. a jet pump is installed in the passage, and a first fluid inlet for driving the jet pump and the air compressor are connected via an air pipe,
A secondary combustion air supply fan is connected to the second fluid inlet of the jet pump, an exhaust hole is opened above the secondary combustion chamber, and a spray nozzle is installed above the secondary combustion chamber and separated from the exhaust hole. A mixing tank for kerosene and alkali is connected to the spray nozzle and the secondary burner via a pump, and the kerosene and alkali are atomized and injected from the spray nozzle, and the gas is A waste plastic gasification incinerator characterized by burning gas from a gasification chamber. 4. The waste plastic gasification incinerator according to claim 3, further comprising a tank exclusively for alkali connected between the kerosene and alkali mixing tank and the spray nozzle via a pump.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2073865A JP2567126B2 (en) | 1990-03-22 | 1990-03-22 | Waste plastic gasification incinerator |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2073865A JP2567126B2 (en) | 1990-03-22 | 1990-03-22 | Waste plastic gasification incinerator |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH03274311A true JPH03274311A (en) | 1991-12-05 |
JP2567126B2 JP2567126B2 (en) | 1996-12-25 |
Family
ID=13530499
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2073865A Expired - Fee Related JP2567126B2 (en) | 1990-03-22 | 1990-03-22 | Waste plastic gasification incinerator |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2567126B2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001059607A (en) * | 1999-08-23 | 2001-03-06 | Meidensha Corp | Method and system for heating matter to be treated |
JP2008190808A (en) * | 2007-02-06 | 2008-08-21 | Soai:Kk | Combustion device |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP6286517B1 (en) * | 2016-12-07 | 2018-02-28 | 株式会社プランテック | Incinerator |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5138189A (en) * | 1974-09-26 | 1976-03-30 | Shizuoka Prefecture | TASODANBOORUNOCHINUKIKAKOHOHO |
JPS5452873A (en) * | 1977-10-04 | 1979-04-25 | Kubota Construction Co | Incinerating treating method of polyvinyl chloride resin |
JPS58139U (en) * | 1981-06-24 | 1983-01-05 | 東北三共有機株式会社 | Complete combustion device |
-
1990
- 1990-03-22 JP JP2073865A patent/JP2567126B2/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5138189A (en) * | 1974-09-26 | 1976-03-30 | Shizuoka Prefecture | TASODANBOORUNOCHINUKIKAKOHOHO |
JPS5452873A (en) * | 1977-10-04 | 1979-04-25 | Kubota Construction Co | Incinerating treating method of polyvinyl chloride resin |
JPS58139U (en) * | 1981-06-24 | 1983-01-05 | 東北三共有機株式会社 | Complete combustion device |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001059607A (en) * | 1999-08-23 | 2001-03-06 | Meidensha Corp | Method and system for heating matter to be treated |
JP2008190808A (en) * | 2007-02-06 | 2008-08-21 | Soai:Kk | Combustion device |
Also Published As
Publication number | Publication date |
---|---|
JP2567126B2 (en) | 1996-12-25 |
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