JP2003320359A - Method and apparatus for pyrolyzing organic waste - Google Patents
Method and apparatus for pyrolyzing organic wasteInfo
- Publication number
- JP2003320359A JP2003320359A JP2002127886A JP2002127886A JP2003320359A JP 2003320359 A JP2003320359 A JP 2003320359A JP 2002127886 A JP2002127886 A JP 2002127886A JP 2002127886 A JP2002127886 A JP 2002127886A JP 2003320359 A JP2003320359 A JP 2003320359A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- organic waste
- pyrolysis
- rotary cylinder
- heating pipe
- 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.)
- Pending
Links
- 239000010815 organic waste Substances 0.000 title claims abstract description 49
- 238000000034 method Methods 0.000 title claims description 21
- 238000000197 pyrolysis Methods 0.000 claims abstract description 87
- 238000010438 heat treatment Methods 0.000 claims abstract description 43
- 238000002407 reforming Methods 0.000 claims abstract description 30
- 239000000428 dust Substances 0.000 claims abstract description 23
- 238000006243 chemical reaction Methods 0.000 claims abstract description 12
- 239000007789 gas Substances 0.000 claims description 95
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 19
- 229910000041 hydrogen chloride Inorganic materials 0.000 claims description 19
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims description 19
- 238000005979 thermal decomposition reaction Methods 0.000 claims description 12
- 239000002918 waste heat Substances 0.000 claims description 11
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 9
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 9
- 239000003054 catalyst Substances 0.000 claims description 6
- 229910002090 carbon oxide Inorganic materials 0.000 claims description 5
- 229910000831 Steel Inorganic materials 0.000 claims 1
- 238000007599 discharging Methods 0.000 claims 1
- 238000001035 drying Methods 0.000 claims 1
- 239000011810 insulating material Substances 0.000 claims 1
- 239000005416 organic matter Substances 0.000 claims 1
- 239000010959 steel Substances 0.000 claims 1
- 239000000446 fuel Substances 0.000 abstract description 12
- 239000002699 waste material Substances 0.000 abstract 2
- 239000000203 mixture Substances 0.000 abstract 1
- 229910052739 hydrogen Inorganic materials 0.000 description 9
- 239000001257 hydrogen Substances 0.000 description 9
- 239000000460 chlorine Substances 0.000 description 8
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 7
- 229910052801 chlorine Inorganic materials 0.000 description 7
- 150000002013 dioxins Chemical class 0.000 description 7
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 5
- 229910002091 carbon monoxide Inorganic materials 0.000 description 5
- 229930195733 hydrocarbon Natural products 0.000 description 5
- 150000002430 hydrocarbons Chemical class 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 229910052799 carbon Inorganic materials 0.000 description 4
- 238000001816 cooling Methods 0.000 description 3
- 230000001877 deodorizing effect Effects 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- 239000004215 Carbon black (E152) Substances 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 238000004880 explosion Methods 0.000 description 2
- 239000003337 fertilizer Substances 0.000 description 2
- 230000006698 induction Effects 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 229920003023 plastic Polymers 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 239000004071 soot Substances 0.000 description 2
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
- 101000604592 Homo sapiens Keratin-like protein KRT222 Proteins 0.000 description 1
- 102100038184 Keratin-like protein KRT222 Human genes 0.000 description 1
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical compound O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 description 1
- 102100031083 Uteroglobin Human genes 0.000 description 1
- 108090000203 Uteroglobin Proteins 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 229910000423 chromium oxide Inorganic materials 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- 239000010800 human waste Substances 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 230000009545 invasion Effects 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 239000000123 paper Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/143—Feedstock the feedstock being recycled material, e.g. plastics
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/40—Valorisation of by-products of wastewater, sewage or sludge processing
Landscapes
- Incineration Of Waste (AREA)
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Hydrogen, Water And Hydrids (AREA)
- Coke Industry (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は下水汚泥、し尿汚
泥、食品汚泥、生ごみ、紙類、プラスチックなどの有機
性廃棄物を熱分解、改質の工程を経て燃料ガスを製造す
る方法及び装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for producing fuel gas through a process of pyrolyzing and reforming organic waste such as sewage sludge, human waste sludge, food sludge, food waste, papers, plastics and the like. It is about.
【0002】[0002]
【発明が解決しようとする課題】有機廃棄物を熱分解す
るに方法としては、熱分解用回転筒体を外部から加熱す
る方法や熱分解用回転筒体に加熱管を装備し、加熱管に
内装したバーナにより加熱管を加熱し、加熱管の輻射熱
により有機性廃棄物を熱分解するといった方法があっ
た。As a method for thermally decomposing organic waste, a method for heating a pyrolysis rotary cylinder from the outside or a method for equipping the pyrolysis rotary cylinder with a heating tube, There has been a method in which a heating pipe is heated by an internal burner and the organic waste is thermally decomposed by radiant heat of the heating pipe.
【0003】ところが熱分解用回転筒体を外部より加熱
すると、熱歪みによって回転筒体の両端に設けられたシ
ールに間隙が生じるという問題点がある。However, when the pyrolysis rotary cylinder is heated from the outside, there is a problem that a gap is created in the seals provided at both ends of the rotary cylinder due to thermal strain.
【0004】シールに間隙が生じると熱分解用回転筒体
が正圧の場合、間隙から熱分解ガスが噴き出し火災や爆
発の危険性があり、他方で負圧の場合は間隙から空気を
吸い込み、火災や爆発の危険があるのである。If a gap is formed in the seal, if the rotary pyrolysis cylinder has a positive pressure, the pyrolysis gas may blow out from the gap, which may cause a fire or explosion. On the other hand, if the seal has a negative pressure, air may be sucked from the gap. There is a risk of fire and explosion.
【0005】また、熱分解用回転筒体内にバーナを内装
した加熱管をもって内部より加熱する方法には加熱管に
内装したバーナの燃料消費量が非常に多い等の問題があ
った。Further, the method of heating from the inside by the heating tube having the burner inside the pyrolysis rotary cylinder has a problem that the fuel consumption of the burner inside the heating tube is very large.
【0006】有機性廃棄物の熱分解は主に熱分解後の残
渣である炭の肥料・土壌改良材などへの有効利用を目的
になされており、熱分解ガスの有効利用は計りずらいも
のであった。その理由としては、熱分解ガスには多量の
タールや粉じんが含まれていること、プラスチックの熱
分解ガスには有害ガスである塩化水素が含まれているこ
となどがあげられる。Pyrolysis of organic waste is mainly aimed at effective use of charcoal, which is the residue after pyrolysis, as fertilizers and soil conditioners, and the effective use of pyrolysis gas is difficult to measure. Met. The reason is that the pyrolysis gas contains a large amount of tar and dust, and the pyrolysis gas of plastic contains hydrogen chloride, which is a harmful gas.
【0007】上記の理由により熱分解ガスは脱臭室(ガ
ス燃焼室とも言う)にて燃焼され、粉じんや塩化水素を
除去した後、大気放散するという処分方法が採られてい
る。For the above reasons, the pyrolysis gas is burned in a deodorizing chamber (also referred to as a gas combustion chamber) to remove dust and hydrogen chloride, and then released into the atmosphere.
【0008】また熱分解ガスに含まれる粉じんや塩化水
素の濃度が低い場合には、廃熱ボイラ、温水ボイラ、空
気加熱器などを脱臭室の後流に装備し、熱回収を計って
いた。Further, when the concentration of dust and hydrogen chloride contained in the pyrolysis gas is low, a waste heat boiler, a hot water boiler, an air heater, etc. were installed downstream of the deodorizing chamber to measure heat recovery.
【0009】いずれにしても熱分解用回転筒体で生成し
た熱分解ガスは脱臭室で焼却処理されており燃焼によっ
て生成するダイオキシン類の発生は免れないものであっ
た。それゆえ熱分解用回転筒体は焼却炉としての範疇で
法規制がなされている。In any case, the pyrolysis gas generated in the pyrolysis rotary cylinder is incinerated in the deodorizing chamber, and the generation of dioxins generated by combustion is unavoidable. Therefore, the pyrolysis rotary cylinder is legally regulated within the category of an incinerator.
【0010】焼却によって発生する猛毒のダイオキシン
類は、塩化水素、未燃カーボン、空気の三要素によって
生成されると考えられている。そこでダイオキシン類対
策としては熱分解ガス中の塩化水素を除去する方法、未
燃カーボンの主体であるタール・煤・炭化水素を除去す
る方法等が講じられている。It is considered that the highly toxic dioxins generated by incineration are produced by the three elements of hydrogen chloride, unburned carbon and air. Therefore, as measures against dioxins, a method of removing hydrogen chloride in the pyrolysis gas, a method of removing tar, soot, and hydrocarbons, which are the main constituents of unburned carbon, have been taken.
【0011】しかしダイオキシン類を完全に除去できる
装置・方法は存在しない。ダイオキシン類の発生を抑制
するには、熱分解ガスを炭化水素の含まないガスに改質
する以外にはないからである。However, there is no apparatus or method capable of completely removing dioxins. This is because the only way to suppress the generation of dioxins is to reform the pyrolysis gas into a hydrocarbon-free gas.
【0012】そこで本発明は上述の従来例の様々な問題
点を解決することが可能な有機性廃棄物の熱分解方法及
び装置を提供することを目的とする。[0012] Therefore, an object of the present invention is to provide a method and apparatus for thermally decomposing organic waste which can solve various problems of the above-mentioned conventional examples.
【0013】[0013]
【課題を解決するための手段】請求項1記載の発明はガ
ス改質室にて改質された高温改質ガスを熱分解用回転筒
体に内装した加熱管内に流し、加熱管の輻射熱によって
有機性廃棄物を熱分解するというものである。According to a first aspect of the present invention, a high temperature reformed gas reformed in a gas reforming chamber is caused to flow into a heating pipe provided inside a rotary cylinder for thermal decomposition, and the radiant heat of the heating pipe is used. It is the thermal decomposition of organic waste.
【0014】高温改質ガスを利用するが故に熱分解用回
転筒体の燃料消費を低減することが可能となるのであ
る。Since the high temperature reformed gas is used, the fuel consumption of the pyrolysis rotary cylinder can be reduced.
【0015】請求項2記載の発明は、有機性廃棄物を―
端から受け入れ他端から排出する熱分解用回転筒体に高
温改質ガスを内部に通した加熱管を内装し、加熱管の輻
射熱を利用し有機性廃棄物を熱分解する装置である。The second aspect of the present invention is directed to organic waste-
This is a device in which a heating pipe having a high-temperature reformed gas passing through is internally provided in a pyrolysis rotary cylinder which is received from the end and discharged from the other end, and radiant heat of the heating pipe is used to thermally decompose organic waste.
【0016】高温改質ガスを利用するが故に熱分解用回
転筒体の燃料消費を低減することが可能となるのであ
る。Since the high temperature reformed gas is used, the fuel consumption of the pyrolysis rotary cylinder can be reduced.
【0017】請求項3記載の発明は高温改質ガスの廃熱
を利用した廃熱ボイラによって高温蒸気を作り、この高
温蒸気を熱分解中の熱分解用回転筒体に吹き込むように
したものである。According to a third aspect of the present invention, a high temperature steam is produced by a waste heat boiler utilizing the waste heat of the high temperature reformed gas, and the high temperature steam is blown into the pyrolysis rotary cylinder during pyrolysis. is there.
【0018】高温蒸気と熱分解ガスが接触することによ
り、下記の表1記載の水性ガス反応が起こり、タール及
び煤は一酸化炭素と水素に分解される。また、熱分解ガ
スは炭素生成率が抑制されて、―酸化炭素及び水素と水
素リッチの低級炭化水素ガスが主体となる。When the high-temperature steam and the pyrolysis gas come into contact with each other, the water-gas reaction shown in Table 1 below occurs, and tar and soot are decomposed into carbon monoxide and hydrogen. Further, the pyrolysis gas has a suppressed carbon production rate, and is mainly composed of carbon oxide and hydrogen, and a hydrogen-rich lower hydrocarbon gas.
【0019】[0019]
【表1】 [Table 1]
【0020】かように熱分解ガスの炭素生成率が抑制さ
れることからダイオキシン類の発生を抑制することが可
能となるのである。尚、有機性廃棄物の熱分解は熱分解
用回転筒体内の温度が約300℃以上で起こり、熱分解
ガスが発生する。また水性ガス反応には400℃以上の
高温蒸気が必要である。As described above, since the carbon production rate of the pyrolysis gas is suppressed, it is possible to suppress the generation of dioxins. The thermal decomposition of the organic waste occurs when the temperature inside the rotary cylinder for thermal decomposition is about 300 ° C. or higher, and thermal decomposition gas is generated. Further, high temperature steam of 400 ° C. or higher is required for the water gas reaction.
【0021】請求項4記載の発明は、熱分解用転筒体に
て製造した熱分解ガスをガス改質室内の加熱管の内部を
通し、この加熱管を外側より加熱することにより、熱分
解ガスをさらに良質なガスに改質することを特徴とす
る。水性ガス反応を起こした熱分解ガスを加熱管に通
し、熱分解ガスの温度を約800℃以上に上げることに
よって水性ガス反応を促進させる。これにより炭化水素
は完全に一酸化炭素と水素にに改質されることになる。
故にこの改質ガスを燃焼させてもダイオキシン類は一切
生成しない良質な燃料となるのである。According to the fourth aspect of the present invention, the pyrolysis gas produced by the pyrolysis cylinder is passed through the inside of the heating pipe in the gas reforming chamber, and the heating pipe is heated from the outside to perform pyrolysis. It is characterized in that the gas is reformed into a higher quality gas. The pyrolysis gas that has undergone the water-gas reaction is passed through a heating pipe, and the temperature of the pyrolysis gas is raised to about 800 ° C. or higher to accelerate the water-gas reaction. As a result, the hydrocarbon is completely reformed into carbon monoxide and hydrogen.
Therefore, even if this reformed gas is burned, it becomes a high-quality fuel that does not produce dioxins at all.
【0022】請求項4記載の発明は有機性廃棄物から良
質な燃料を製造する有機性廃棄物の熱分解方法であって
請求項5記載の発明は請求項4記載の発明を実現した装
置の構造である。The invention according to claim 4 is a method for thermally decomposing an organic waste for producing a high quality fuel from the organic waste, and the invention according to claim 5 is an apparatus for realizing the invention according to claim 4. It is a structure.
【0023】請求項6記載の発明は、請求項5記載の発
明において加熱管にニッケル等の触媒を充填するもので
ある。これにより加熱管のみの場合の水性ガスの最適反
応温度は1300から1400℃であるのに対し、80
0〜900℃に下げることができ加熱管の長寿命化と省
エネルギー化が計られるものである。According to a sixth aspect of the invention, in the fifth aspect of the invention, the heating pipe is filled with a catalyst such as nickel. As a result, the optimum reaction temperature of water gas in the case of only the heating tube is 1300 to 1400 ° C.
The temperature can be lowered to 0 to 900 ° C., and the life of the heating tube can be extended and the energy can be saved.
【0024】請求項7記載の発明は、請求項1、2及び
3記載の発明である高温蒸気を利用した熱分解用回転筒
体(回転熱分解室とも言う)と、請求項4、5及び6記載
の発明であるガス改質室に、―酸化炭素を水素に転換す
る―酸化炭素転換室(公知)を付加することによって可能
にした有機性廃棄物から水素燃料を製造する方法であ
る。The invention according to claim 7 is a rotary cylinder for pyrolysis (also referred to as a rotary pyrolysis chamber) utilizing high-temperature steam, which is the invention according to claims 1, 2 and 3, and claims 4, 5 and A method for producing hydrogen fuel from organic waste made possible by adding a carbon oxide conversion chamber (known) for converting carbon oxide to hydrogen in the gas reforming chamber of the invention described in 6.
【0025】有機性廃棄物には塩素が含まれていること
が多く、有機性廃棄物を熱分解すると塩化水素ガスに変
わり、熱分解ガスに含まれてガス改質室側に排出され
る。塩化水素ガスは有害ガスとしての排出基準があり、
大気中に排出する塩化水素ガスの濃度は排出基準以下に
する必要があることは言うまでもないが、塩化水素ガス
は腐食性が強く、装置の寿命を考えると早い段階で除去
する必要がある。そこで請求項8記載の発明は、塩化水
素ガス除去装置を熱分解用回転筒体とガス改質室の間に
配備し、熱分解時に発生する塩素ガスを早い段階で除去
することによって装置全体の延命化を計ったのである。Chlorine is often contained in the organic waste, and when the organic waste is thermally decomposed, it is converted into hydrogen chloride gas, which is contained in the thermally decomposed gas and discharged to the gas reforming chamber side. Hydrogen chloride gas has emission standards as harmful gas,
Needless to say, the concentration of hydrogen chloride gas discharged into the atmosphere needs to be below the emission standard, but hydrogen chloride gas is highly corrosive and needs to be removed at an early stage considering the life of the device. Therefore, according to the invention of claim 8, a hydrogen chloride gas removing device is provided between the rotary cylinder for pyrolysis and the gas reforming chamber, and chlorine gas generated during the pyrolysis is removed at an early stage so that the entire device can be removed. The life was extended.
【0026】また、請求項8記載の発明によれば塩化水
素除去装置内に加熱管を通すことによって、塩化水素ガ
ス除去剤を加熱し、除去効率を上げるのと同時に、熱分
解用回転筒体よりガス改質室側へ熱分解ガスと同伴する
タール分を熱分解することが可能となる。更には粉じん
を捕捉することも可能となるのである。Further, according to the invention of claim 8, the hydrogen chloride gas removing agent is heated by passing a heating pipe through the hydrogen chloride removing device to improve the removal efficiency, and at the same time, the rotary cylinder for pyrolysis. As a result, it becomes possible to thermally decompose the tar component that accompanies the pyrolysis gas toward the gas reforming chamber side. Furthermore, it becomes possible to capture dust.
【0027】有機性廃棄物には、塩素を含まないものや
含んでいても微量で排出基準以下で、かつ腐食性も問題
にならないものも多々あり、これら有機性廃棄物には、
塩化水素除去装置は不要であるが、熱分解用回転筒体で
の熱分解時、熱分解ガスに同伴するタールや粉じんが加
熱管を閉塞する恐れがある。請求項9記載の発明は、熱
分解用回転筒体の熱分解ガス出口に集塵用サイクロンを
設置し、加熱管に入る前にダールや粉じんを捕捉するも
のである。There are many organic wastes that do not contain chlorine, and even if they contain chlorine, the trace amount is less than the emission standard and the corrosiveness does not pose any problem.
Although a hydrogen chloride removing device is not required, tar and dust entrained in the pyrolysis gas may block the heating pipe during pyrolysis in the rotary pyrolysis cylinder. According to the ninth aspect of the present invention, a dust collecting cyclone is installed at the pyrolysis gas outlet of the pyrolysis rotary cylinder, and the dahl and dust are captured before entering the heating pipe.
【0028】請求項10記載の発明は捕捉したタール及
び粉じんを有機性廃棄物の熱分解用回転筒体の投入機側
に戻し、新たに投入する有機性廃棄物と混ぜ合わせて再
投入し、熱分解用回転筒体で再び熱分解することにより
捕捉したタールや粉じんを系外に取りだすことなしにタ
ールや粉じんの大幅な減量化を達成した集塵用サイクロ
ンの構造である。According to the tenth aspect of the invention, the captured tar and dust are returned to the charging machine side of the rotary cylinder for pyrolysis of the organic waste, mixed again with the organic waste to be charged again, and charged again. This is a structure of a cyclone for dust collection that achieves a significant reduction of tar and dust without removing the tar and dust captured by pyrolysis again with the rotary cylinder for pyrolysis to the outside of the system.
【0029】[0029]
【発明の実施の形態】以下、本発明の―実施の形態を図
1、図2に基づいて説明する。BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to FIGS.
【0030】図1は、本発明の塩素を含む有機性廃棄物
の熱分解方法とその装置を示すフロー図であり、図2は
本発明の塩素含有量の少なく粉じんが飛散しやすい有機
性廃棄物の熱分解方法とその装置を示すフロー図であ
る。FIG. 1 is a flow chart showing a method and apparatus for thermally decomposing chlorine-containing organic waste according to the present invention, and FIG. 2 is an organic waste according to the present invention with a low chlorine content and dust easily scattered. It is a flowchart which shows the thermal decomposition method of an object, and its apparatus.
【0031】図1において、コンべア3に乗せられた有
機性廃棄物はホッパー4に投入され、二重ダンパーの上
段ダンパー5の上面に落とし込まれる。この時、下段ダ
ンパー6は閉じた状態にある。上段ダンパー5を開き、
有機性廃棄物を下段ダンパー6の上面に落とし込む、こ
の後、上段ダンパー5を閉じ、下段ダンパー6を開き、
有機性廃棄物は二重ダンパーの下部に設けられた破砕機
7に落とし込まれる。この二重ダンパー動作は外気から
の空気の侵入をできるだけ防ぐ目的で行われる。破砕機
7に落とし込まれた有機性廃棄物は破砕機7にて破砕さ
れ、嵩を小さくした状態で、熱分解用回転筒体に取り付
けられた投入用スクリュウコンべア8に送られる。In FIG. 1, the organic waste placed on the conveyor 3 is thrown into the hopper 4 and dropped on the upper surface of the upper damper 5 of the double damper. At this time, the lower damper 6 is in a closed state. Open the upper damper 5,
Drop the organic waste on the upper surface of the lower damper 6, then close the upper damper 5 and open the lower damper 6,
The organic waste is dropped into the crusher 7 provided under the double damper. This double damper operation is performed for the purpose of preventing invasion of air from the outside air as much as possible. The organic waste dropped into the crusher 7 is crushed by the crusher 7 and sent to the charging screw conveyor 8 attached to the pyrolysis rotary cylinder in a state where the bulk is reduced.
【0032】有機性廃棄物が熱分解用回転筒体に投入さ
れる前に熱分解用回転筒体1およびガス改質室2の内部
はバーナ等によって予熱されており、熱分解用回転筒体
の内部は300〜750℃の温度に設定されており、廃
熱ボイラー9も立ち上がっており、廃熱ボイラー9で作
られた高温蒸気はすでに熱分解用回転筒体に導入された
状態にある。またガス改質室2も800〜1300℃に
設定されている。Before the organic waste is charged into the pyrolysis rotary cylinder, the interiors of the pyrolysis rotary cylinder 1 and the gas reforming chamber 2 are preheated by a burner or the like, and the pyrolysis rotary cylinder is Is set to a temperature of 300 to 750 ° C., the waste heat boiler 9 is also activated, and the high temperature steam produced by the waste heat boiler 9 is already introduced into the pyrolysis rotary cylinder. The gas reforming chamber 2 is also set to 800 to 1300 ° C.
【0033】また、有機性廃棄物が熱分解用回転筒体に
入る前には誘引通風機10を含め装置の全てが起動して
おり、熱分解用回転筒体1に投入された有機性廃棄物は
熱分解用回転筒体の出口端部に行くまでに熱分解され、
熱分解ガスは熱分解用回転筒体1を出た後、塩化水素除
去装置11の塩化水素除去剤12の中を通り、ガス改質
室内に設けられたガス改質室加熱管13に入り、ガス改
質室にて800℃以上に加熱され、再び、熱分解用回転
筒体内に設けられた熱分解回転筒体加熱管14内を通
り、誘引通風機10によって廃熱ボイラー9側に引き出
される。Before the organic waste enters the pyrolysis rotary cylinder, all the devices including the induction fan 10 are activated, and the organic waste thrown into the pyrolysis rotary cylinder 1 is discharged. The thing is pyrolyzed by the time it goes to the outlet end of the pyrolysis rotary cylinder,
After the pyrolysis gas leaves the rotary pyrolysis cylinder 1, the pyrolysis gas passes through the hydrogen chloride removing agent 12 of the hydrogen chloride removing apparatus 11 and enters the gas reforming chamber heating pipe 13 provided in the gas reforming chamber. It is heated to 800 ° C. or higher in the gas reforming chamber, and again passes through the pyrolysis rotary cylinder heating pipe 14 provided in the pyrolysis rotary cylinder, and is drawn to the waste heat boiler 9 side by the induced draft fan 10. .
【0034】ガス改質室2に内装された加熱管13と熱
分解用回転筒体1に内装された加熱管14とは―体の管
であり、ガス改質室の加熱管内で加熱された熱分解ガス
は、改質し、熱分解用回転筒体の加熱管内を通り廃熱ボ
イラー側に引き出される。熱分解用回転筒体の加熱管と
中を流れる改質ガスは800℃以上の高温になっており
熱分解用回転筒体内の有機性廃棄物を熱分解するに充分
な熱源となり、熱分解用回転筒体バーナ15の熱源はも
はや不要となる。従って、常時の熱源としては、ガス改
質室に設けたバーナ16のみとなる。The heating tube 13 installed in the gas reforming chamber 2 and the heating tube 14 installed in the rotary pyrolysis cylinder 1 are body tubes and are heated in the heating tube of the gas reforming chamber. The pyrolysis gas is reformed, passes through the heating pipe of the rotary pyrolysis cylinder, and is drawn to the waste heat boiler side. The heating tube of the pyrolysis rotary cylinder and the reformed gas flowing through it are at a high temperature of 800 ° C or higher, and serve as a sufficient heat source for pyrolyzing the organic waste in the pyrolysis rotary cylinder. The heat source of the rotary cylinder burner 15 is no longer needed. Therefore, the burner 16 provided in the gas reforming chamber is the only heat source at all times.
【0035】また、ガス改質室1の加熱管13の内部に
二ッケル触媒等の触媒26を充填することによって熱分
解ガスの改質温度を下げることができる。By filling the inside of the heating pipe 13 of the gas reforming chamber 1 with a catalyst 26 such as a Nikkell catalyst, the reforming temperature of the pyrolysis gas can be lowered.
【0036】炭化水素や若干のタール分を含む熱分解ガ
スは、水性ガス反応によって一酸化炭素と水素主体のガ
スに改質され、この改質ガスは廃熱ボイラー9を通り、
廃熱ボイラー9にて熱回収され、冷却器19、気液分離
ドラム18によって冷却されることによって余剰の水が
取り除かれ、さらに改質ガスに同伴する水のミスト(液
滴)は気夜分離ドラムにて取り除かれ、―端ガスタンク
27に貯められた後、ブースター30によって加圧圧送
し、発電機24等の熱源となす。また、熱分解用回転筒
体バーナ15やガス改質室バーナ16の燃料としも使用
てきる。The pyrolysis gas containing hydrocarbons and a small amount of tar is reformed into a gas composed mainly of carbon monoxide and hydrogen by a water gas reaction, and this reformed gas passes through a waste heat boiler 9,
The waste heat boiler 9 recovers heat, and the cooler 19 and the gas-liquid separation drum 18 cool it to remove excess water, and the mist (droplets) of water that accompanies the reformed gas is separated overnight. After being removed by the drum and stored in the end gas tank 27, it is pressurized and pressure-fed by the booster 30 to serve as a heat source for the generator 24 and the like. It can also be used as fuel for the pyrolysis rotary cylinder burner 15 and the gas reforming chamber burner 16.
【0037】さらに改質ガスを酸化鉄を主成分とし、酸
化クロムを促進剤とした触媒を有し温度を500℃程度
に設定した一酸化炭素転換室23を通すことによってや
はり水性ガス反応によって一酸化炭素を水素と二酸化炭
素に転換し、二酸化炭素は水を持って溶解除去するかア
ルカリによって吸収除去することによって発電機24や
燃料電池26の水素燃料として使用できることから地球
温暖化防止の―助となる。Further, the reformed gas is passed through the carbon monoxide conversion chamber 23 having a catalyst containing iron oxide as a main component and chromium oxide as a promoter and the temperature is set to about 500 ° C. It can be used as hydrogen fuel for the generator 24 and the fuel cell 26 by converting carbon oxide into hydrogen and carbon dioxide, and dissolving or removing carbon dioxide with water or absorbing and removing it with an alkali, which helps prevent global warming. Becomes
【0038】回収した余剰の水には炭化水素やタール等
の油分や有害物質が含まれていないことからドレントラ
ム28に貯めた後、噴霧ポンプ29によって冷却塔17
の噴霧ノズル31に送り、ガス改質室バーナ排ガスの冷
却水として利用する。Since the surplus water recovered does not contain oils and harmful substances such as hydrocarbons and tar, it is stored in the drain ram 28 and then the cooling tower 17 is supplied by the spray pump 29.
And used as cooling water for the exhaust gas of the gas reforming chamber burner.
【0039】ガス改質室1のバーナ16の排ガスは冷却
塔17にて約200℃に冷却された後、排気される。The exhaust gas from the burner 16 in the gas reforming chamber 1 is cooled to about 200 ° C. in the cooling tower 17 and then exhausted.
【0040】図2の発明は、熱分解用回転筒体1に集塵
用サイクロン20を取り付け熱分解用回転筒体1より排
出する熱分解ガスに同伴する粉じんやタール分を集塵用
サイクロンにて捕捉して、加熱管での閉塞を防止する。
集塵用サイクロンで捕捉した集塵物は投入用スクリュウ
コンべア8に返し、有機性廃棄物と混合し、熱分解用回
転筒体に再投入し、再び熱分解することによって粉じん
やタール分減量化を計った。In the invention of FIG. 2, the dust-collecting cyclone 20 is attached to the pyrolysis rotary cylinder 1, and the dust and tar entrained in the pyrolysis gas discharged from the pyrolysis rotary cylinder 1 is converted into a dust-collecting cyclone. To prevent blockage in the heating tube.
The dust collected by the cyclone for dust collection is returned to the screw conveyor 8 for input, mixed with the organic waste, re-input to the rotary cylinder for thermal decomposition, and again thermally decomposed to remove dust and tar. The weight was reduced.
【0041】熱分解用回転筒体1での熱分解後の残渣
(炭化物)は熱分解用回転筒体の端物より自動的に排出す
るが、これを水冷コンべア21によって冷却し、容器2
2に袋詰めして、肥料や土壌改良材として有効利用す
る。Residue after pyrolysis in the pyrolysis rotary cylinder 1
(Carbide) is automatically discharged from the end product of the pyrolysis rotary cylinder, but this is cooled by the water-cooled conveyor 21 and the container 2
Pack it in 2 and use it effectively as fertilizer and soil conditioner.
【図1】 本発明による塩素を含む有機性廃棄物の熱分
解方法とその装置を示すフロー図。FIG. 1 is a flow chart showing a method and apparatus for thermally decomposing chlorine-containing organic waste according to the present invention.
【図2】 発明による塩素含有量が少なく粉じんが飛散
しやすい有機性廃棄物の熱分解方法とその装置を示すフ
ロー図。FIG. 2 is a flow chart showing a method and apparatus for thermally decomposing an organic waste having a low chlorine content and easy dust scattering according to the present invention.
1 熱分解用回転筒体 2 ガス改質室 3 コンべア 4 ホッパ 5 上段ダンパー 6 下段ダンパー 7 破砕機 8 投入用スクリュウコンべア 9 廃熱ボイラー 10 誘引通風機 11 塩化水素除去装置 12 塩化水素除去剤 13 ガス改質室加熱管 14 熱分解用回転筒体加熱管 15 熱分解用回転筒体用バーナ 16 ガス改質室用バーナ 17 冷却塔 18 気液分離ドラム 19 冷却器 20 集塵用サイクロン 21 水冷コンべア 22 容器 23 一酸化炭素転換室 24 発電ボイラー 25 燃料電池 26 触媒 27 ガスタンク 28 ドレンドラム 29 噴霧ポンプ 30 ブースター 31 噴霧ノズル 1 Pyrolysis rotary cylinder 2 gas reforming room 3 Conveyor 4 hoppers 5 Upper damper 6 Lower damper 7 crusher 8 Input screw conveyor 9 Waste heat boiler 10 induction fan 11 Hydrogen chloride removal device 12 Hydrogen chloride remover 13 Gas reforming chamber heating pipe 14 Rotary tube heating tube for pyrolysis 15 Burner for rotary cylinder for pyrolysis 16 Burner for gas reforming room 17 Cooling tower 18 Gas-liquid separation drum 19 Cooler 20 Cyclone for dust collection 21 Water-cooled conveyor 22 containers 23 Carbon monoxide conversion room 24 power generation boiler 25 fuel cells 26 catalyst 27 gas tank 28 drain drum 29 Spray pump 30 boosters 31 spray nozzle
フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 11/10 ZAB C02F 11/10 ZABZ 4G140 C10B 53/00 C10B 53/00 A 4H012 B C10J 3/00 C10J 3/00 A F F23G 5/027 F23G 5/027 Z 5/14 5/14 F 5/20 5/20 A 5/44 5/44 Z Fターム(参考) 3K061 AA07 AB02 AC01 AC02 AC12 AC13 BA01 CA01 CA07 FA04 FA10 FA12 KA02 KA21 KA23 3K065 AA24 AB01 AC01 AC02 AC12 AC13 BA01 HA02 3K078 BA08 CA02 CA07 4D004 AA02 AA03 AA07 AA12 AB06 BA03 BA04 BA06 CA04 CA27 CA47 CB09 CB13 CB34 CB36 CC09 4D059 AA02 AA03 AA07 BB03 BB14 BK11 CB06 CC01 CC10 4G140 BA02 BB03 4H012 HA03 HB03 HB10 Front page continuation (51) Int.Cl. 7 Identification code FI theme code (reference) C02F 11/10 ZAB C02F 11/10 ZABZ 4G140 C10B 53/00 C10B 53/00 A 4H012 B C10J 3/00 C10J 3/00 A F F23G 5/027 F23G 5/027 Z 5/14 5/14 F 5/20 5/20 A 5/44 5/44 Z F term (reference) 3K061 AA07 AB02 AC01 AC02 AC12 AC13 BA01 CA01 CA07 FA04 FA10 FA12 KA02 KA21 KA23 3K065 AA24 AB01 AC01 AC02 AC12 AC13 BA01 HA02 3K078 BA08 CA02 CA07 4D004 AA02 AA03 AA07 AA12 AB06 BA03 BA04 BA06 CA04 CA27 CA47 CB09 CB13 CB34 CB36 CC09 4D059 AA02 AA03 AA07 BB03 BB14 BK11 CB06 CC01 CC10 4G140 BA02 BB03 4H012 HA03 HB03 HB10
Claims (10)
後、高温改質ガスを内部に通した加熱管の輻射熱により
加熱し、熱分解する有機性廃棄物の熱分解方法。1. A method of thermally decomposing an organic waste, which comprises heating the organic waste as it is or after drying it by radiant heat of a heating pipe having a high-temperature reformed gas passing through it, and thermally decomposing it.
備し、有機性廃棄物を―端から受け入れて他端から排出
する間に有機性廃棄物を熱分解する熱分解用回転筒体よ
り成る有機性廃棄物の熱分解装置。2. A rotary tube for pyrolysis, which is internally equipped with a heating tube through which high-temperature gas passes, and which pyrolyzes organic waste while receiving it from one end and discharging it from the other end. Pyrolysis device for organic waste consisting of the body.
該ボイラから発生した高温蒸気を熱分解用回転筒体に導
入し、有機性廃棄物の熱分解の促進と水性ガス反応によ
り熱分解ガスを製造することを特徴とする有機性廃棄物
の熱分解方法。3. A boiler is heated by utilizing waste heat of a heating pipe,
Pyrolysis of organic waste, characterized in that high-temperature steam generated from the boiler is introduced into a rotary cylinder for pyrolysis to promote pyrolysis of the organic waste and produce a pyrolysis gas by a water gas reaction. Method.
ガス改質室内の加熱管の内部を通し、この加熱管を外側
より加熱することにより、熱分解ガスをさらに良質なガ
スに改質することを特徴とする有機性廃棄物の熱分解方
法。4. A pyrolysis gas produced by a pyrolysis cylinder is passed through the inside of a heating pipe in a gas reforming chamber, and the heating pipe is heated from the outside so that the pyrolysis gas has a higher quality. A method for thermally decomposing organic waste, characterized by reforming into organic matter.
であるガス改質室内に加熱管を内装し、回収した改質ガ
スをバーナを用いて燃焼させ加熱管を加熱することを特
徴とする有機性廃棄物の熱分解装置。5. A heating pipe is provided inside a gas reforming chamber, which is a casing of a steel sheet lined with a refractory heat insulating material, and the recovered reformed gas is burned using a burner to heat the heating pipe. Thermal decomposition equipment for organic waste.
ル等の触媒を充填したことを特徴とする請求項5記載の
有機性廃棄物の熱分解装置。6. The apparatus for thermally decomposing organic waste according to claim 5, wherein a heating tube equipped in the gas reforming chamber is filled with a catalyst such as Nikkell.
及び―酸化炭素転換室の三室の組み合わせにより有機性
廃棄物から水素ガスを生成する有機性廃棄物の熱分解方
法。7. A method for thermally decomposing an organic waste, wherein hydrogen gas is produced from the organic waste by a combination of a thermal decomposition chamber using high temperature steam, a gas reforming chamber and a carbon oxide conversion chamber.
に塩化水素除去装置を設け、この塩化水素除去装置の中
に高温の改質ガスを通した加熱管を配備したことを特徴
とする有機性廃棄物の熱分解装置。8. A hydrogen chloride removing device is provided between the pyrolysis rotary cylinder and the gas reforming chamber, and a heating pipe through which high-temperature reformed gas is passed is provided in the hydrogen chloride removing device. Pyrolysis device for organic waste.
塵用サイクロンを設けたことを特徴とする有機性廃棄物
の熱分解装置。9. An apparatus for thermally decomposing organic waste, characterized in that a cyclone for collecting dust is provided at the thermally decomposing gas outlet of the rotary cylinder for thermal decomposition.
じんを熱分解用回転筒体の投入機に戻し、新たに投入す
る有機性廃棄物と混ぜ合わせて熱分解用回転筒体に投入
し、再び熱分解するシステムとした請求項9記載の有機
性廃棄物の熱分解装置。10. The tar and dust collected by the cyclone for dust collection are returned to the throwing machine of the rotary cylinder for thermal decomposition, mixed with the newly introduced organic waste, and charged into the rotary cylinder for thermal decomposition. The apparatus for thermally decomposing organic waste according to claim 9, which is a system for thermally decomposing again.
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|---|---|---|---|
| JP2002127886A JP2003320359A (en) | 2002-04-30 | 2002-04-30 | Method and apparatus for pyrolyzing organic waste |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2002127886A JP2003320359A (en) | 2002-04-30 | 2002-04-30 | Method and apparatus for pyrolyzing organic waste |
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| CN102141251A (en) * | 2010-02-01 | 2011-08-03 | 株式会社东芝 | Combustion device |
| JP2013534265A (en) * | 2010-08-19 | 2013-09-02 | 西峡龍成特種材料有限公司 | Electrothermal carbon material decomposition equipment |
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