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JP2017225938A - Treatment device of organic waste - Google Patents

Treatment device of organic waste Download PDF

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JP2017225938A
JP2017225938A JP2016124357A JP2016124357A JP2017225938A JP 2017225938 A JP2017225938 A JP 2017225938A JP 2016124357 A JP2016124357 A JP 2016124357A JP 2016124357 A JP2016124357 A JP 2016124357A JP 2017225938 A JP2017225938 A JP 2017225938A
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pressure
container
organic waste
temperature
waste
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修右 大関
Shusuke Ozeki
修右 大関
昌裕 佐藤
Masahiro Sato
昌裕 佐藤
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

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Abstract

PROBLEM TO BE SOLVED: To provide a treatment device of organic wastes which can be disposed after attaining aseptic condition and detoxication by the disinfection or sterilization of microorganisms and disease germs bred or adhered on the organic wastes.SOLUTION: A treatment device of organic wastes where the organic wastes are hydrolyzed while being agitated under high temperature and high pressure environments in a pressure-resistant container 1, thermally decomposed and carbonized includes: a steam supply means 9 supplying high temperature saturated steam into the container 1; a temperature adjusting means 11 adjusting temperature in the container 1 to 220-260°C; a pressure adjusting means 10 adjusting pressure in the container 1 to 2-3 MPa by an on-off valve; a steam discharge means 14 forcibly discharging steam generated in the container 1; and an agitation means 6 disposed with a shaft 7 agitating charged wastes in the container 1 and being penetrated in the container 1.SELECTED DRAWING: Figure 1

Description

本発明は、焼却や埋立てなどにより処理されていた従来の有機系廃棄物を、水蒸気による高温・高圧の環境下で分解処理する廃棄物処理装置に関し、特に使用済みの敷き藁や医療廃棄物の分解処理に際しそれらに付着している病原菌や微生物、ウィルス、細菌、雑菌を滅菌ないし死滅させることができる有機系廃棄物の処理装置に関する。   The present invention relates to a waste treatment apparatus for decomposing and treating a conventional organic waste that has been treated by incineration or landfilling in a high-temperature and high-pressure environment using water vapor, and particularly used litter and medical waste. The present invention relates to an organic waste processing apparatus capable of sterilizing or killing pathogenic bacteria, microorganisms, viruses, bacteria, and various germs adhering to them during decomposition processing.

従来から廃タイヤなどのゴム類等、リサイクルシステムがある程度完成している新聞古紙や分別された廃プラスチックなどの場合は別として、例えば、古紙や紙屑などの紙類、使用済みのプラスチック製容器や袋、ペットボトルなどのプラスチック類、或いはレストランや食堂、各家庭などからでる生ゴミ類といった有機系廃棄物は、通常、焼却炉で焼却処分したり、焼却できないものは地中に埋設して処分されていた。   Aside from conventional newspapers and recycled plastics that have been recycled to some extent, such as rubber from waste tires, etc., for example, paper such as used paper and waste paper, used plastic containers, Organic waste such as plastics such as bags and plastic bottles, or garbage from restaurants, canteens, and households are usually incinerated in an incinerator, or those that cannot be incinerated are buried in the ground. It had been.

また、上記以外の有機系廃棄物として、馬や牛、或いは、豚などを移送、運搬するときにコンテナ内や車輌内の床面に敷く敷き藁がある。そして敷き藁には、馬などが敷き藁に直接排便等するため、敷き藁を処分するときに糞や尿も一緒に処分する必要がある。しかし、このような敷き藁には微生物や雑菌が繁殖しているため、焼却炉で焼却処分すると、微生物や雑菌の一部が死滅しないで、排煙と一緒に大気中に放出される、或いは焼却灰中に残っているおそれがある。   In addition, organic waste other than the above is a litter laid on the floor of a container or vehicle when transporting or transporting horses, cattle or pigs. In addition, since horses and the like defecate directly on the mattress, it is necessary to dispose of feces and urine together with the mattress. However, microorganisms and other germs breed on such a litter, so when incinerated in an incinerator, some of the microorganisms and germs are not killed and are released into the atmosphere along with smoke. May remain in incineration ash.

更に、上記以外の有機系廃棄物として、病院などの医療機関およびその医療現場並びに老人保健施設などの介護施設から出る使用済みの包帯、綿、おむつ、シーツなどの布もしくは紙類の医療廃棄物がある。これらは専門の業者が回収しているが、回収されたものをそのまま焼却炉で焼却すると、敷き藁の場合と同様に、病原菌や雑菌、ウィルスなどが大気中に放出される、或いは焼却灰中に残っているおそれがあるため、焼却前に消毒や殺菌処理をする必要がある。   Furthermore, as organic waste other than the above, used bandages, cotton, diapers, sheets, and other medical waste such as hospitals and other medical institutions and their medical sites and nursing facilities such as geriatric health facilities There is. These are collected by specialists, but if the collected materials are incinerated as they are in an incinerator, pathogens, germs, viruses, etc. are released into the atmosphere as in the case of litter, or in incineration ash Therefore, it is necessary to disinfect and sterilize before incineration.

しかし、最近は地球環境保全の観点から、有機系廃棄物の焼却炉による焼却処分に対する風当たりが強く、また、焼却炉による廃プラスチック等の焼却処分は、焼却炉の損傷、或いはダイオキシンなどの有害物質が発生するおそれがあるため、法令や条例などにより、焼却炉による焼却処分が厳しく規制されている。   However, recently, from the viewpoint of protecting the global environment, there has been a strong wind perception of incineration of organic waste in an incinerator, and incineration of waste plastics in an incinerator can cause damage to the incinerator or harmful substances such as dioxins. Therefore, incineration with an incinerator is strictly regulated by laws and regulations.

そのようなことから、有機系廃棄物を焼却炉による焼却以外の方法で処分する方法と装置の開発が行われており、その一例として、高温・高圧の水蒸気または亜臨界水もしくは超臨界水を用いた水熱反応を利用した処理システム、処理方法または処理装置が、例えば特許第3832587号公報(特許文献1)、特開平10−147662号公報(特許文献2)、特許第3440835号公報(特許文献3)および/または特開2004−290819号公報(特許文献4)にそれぞれ開示されている。   For this reason, methods and devices for disposal of organic waste by methods other than incineration using an incinerator have been developed. For example, high-temperature and high-pressure steam, subcritical water, or supercritical water can be used. The processing system, the processing method, or the processing apparatus using the hydrothermal reaction used are, for example, Japanese Patent No. 3832587 (Patent Document 1), Japanese Patent Application Laid-Open No. 10-147661 (Patent Document 2), and Japanese Patent No. 3440835 (Patent Document). Document 3) and / or Japanese Patent Application Laid-Open No. 2004-290819 (Patent Document 4), respectively.

特許文献1に開示されているシステムは、廃棄物その他の一般材料を高温・高圧の環境下で発熱成型体として再利用できるように処理するためのもので、優れたシステムではあるが、処理後に耐圧容器を開いたとき内部のガスや蒸気等が外部に放出されてしまうため、病原菌や微生物、雑菌などが残存していたとき一緒に大気中に拡散されてしまうおそれがあり、この点で改良の余地があった。また、特許文献2に開示されている分解処理方法、装置も水熱反応を利用し、臨界圧力以下の温度で難分解性廃棄物を分解処理するものであるが、連続式であるため、装置が複雑になってしまうという問題があった。更に、特許文献3に開示されている有機性廃棄物の処理方法は、水の超臨界温度以上で超臨界圧力未満に設定された高温高圧水蒸気中で酸化処理する方法であるが、設定温度が500℃以上、圧力が5MPa〜22MPaと高いため、それに耐え得る装置の開発が難しく、コストもかかるという問題があった。次に、特許文献4に開示されている高温高圧処理装置は、超臨界水または亜臨界水の状態下で有機性廃棄物を連続的に酸化処理するものであるが、酸化分解反応に好ましい亜臨界水の処理条件は、温度250℃以上、処理圧力5〜10MPaであるため、この条件で連続的に酸化処理するための装置の開発が難しく、コストがかかり過ぎるという問題があった。   The system disclosed in Patent Document 1 is for processing waste and other general materials so that they can be reused as a heat-generating molded body in a high-temperature and high-pressure environment. When the pressure vessel is opened, internal gas and vapors are released to the outside, so if pathogens, microorganisms, germs, etc. remain, they may be diffused into the atmosphere. There was room for. In addition, the decomposition method and apparatus disclosed in Patent Document 2 also uses hydrothermal reaction to decompose hardly decomposable waste at a temperature lower than the critical pressure. There was a problem that became complicated. Furthermore, the organic waste processing method disclosed in Patent Document 3 is a method of oxidizing in high-temperature and high-pressure steam set to a temperature higher than the supercritical temperature of water and lower than the supercritical pressure. Since the pressure is as high as 500 ° C. or higher and 5 MPa to 22 MPa, there is a problem that it is difficult to develop an apparatus capable of withstanding it and costs high. Next, the high-temperature and high-pressure treatment device disclosed in Patent Document 4 continuously oxidizes organic waste in the state of supercritical water or subcritical water. Since the critical water treatment conditions are a temperature of 250 ° C. or higher and a treatment pressure of 5 to 10 MPa, it is difficult to develop an apparatus for continuous oxidation treatment under these conditions, and there is a problem that costs are excessive.

また、上記特許文献1〜4に開示されている発明は、水熱反応を用いて有機系廃棄物を分解するという点で共通しているが、有機系廃棄物に病原菌や微生物、雑菌が付着し、繁殖している場合等に対する対策が充分になされておらず、例えば、敷き藁に繁殖した微生物や雑菌、医療廃棄物に付着した病原菌を滅菌もしくは殺菌することまでは検証されておらず、これらを大気中に拡散させないような装置構成にはなっていない。   In addition, the inventions disclosed in Patent Documents 1 to 4 are common in that organic waste is decomposed using a hydrothermal reaction, but pathogens, microorganisms, and germs are attached to the organic waste. However, measures against cases of breeding have not been taken sufficiently, for example, microorganisms and germs that have propagated on the litter are not verified until sterilization or sterilization of pathogens attached to medical waste, The device configuration is not such that they do not diffuse into the atmosphere.

特許第3832587号公報Japanese Patent No. 3832587 特開平10−147662号公報JP-A-10-147762 特許第3440835号公報Japanese Patent No. 3440835 特開2004−290819号公報JP 2004-290819 A

本発明は、従来の有機系廃棄物の処理装置には上記のような問題点があることに鑑み、有機系廃棄物、特に敷き藁や医療廃棄物等を、それらに繁殖または付着した微生物や病原菌を滅菌もしくは死滅させることにより、無菌化、無害化した上で処分することができる従来にない新たな有機系廃棄物の処理装置を提供することをその課題とするものである。   In view of the above-mentioned problems in conventional organic waste treatment apparatuses, the present invention is directed to microorganisms that propagate or adhere to organic waste, particularly litter, medical waste, etc. It is an object of the present invention to provide an unprecedented new organic waste processing apparatus which can be disposed of after sterilization or detoxification by sterilizing or killing pathogenic bacteria.

上記課題を解決することを目的としてなされた本発明処理装置の構成は、耐圧容器内において有機系廃棄物を高温・高圧の環境下で攪拌しながら加水分解すると共に、熱分解し、炭化して処理する廃棄物の処理装置であって、前記容器内に高熱の飽和水蒸気を供給するための水蒸気供給手段と、前記容器内の温度を調節するための温度調節手段と、該容器内の圧力を開閉弁により調節する圧力調節手段と、該容器内に生じる水蒸気を強制排出する水蒸気排出手段と、投入された廃棄物を前記容器内で攪拌するため軸が当該容器内を貫通して設けられた攪拌手段を備え、前記容器内の温度を前記温度調節手段により220〜260℃に調節し、前記容器内の圧力を前記圧力調節手段により2〜3MPaに調節し、前記水蒸気供給手段により高熱の飽和水蒸気を供給し、かつ前記有機系廃棄物を攪拌することにより、容器内の水蒸気を強制排出しながら乾燥させて前記処理をすると共に、該処理の後、前記圧力調整手段により前記容器内の圧力を大気圧以下に調節して、処理された前記有機系廃棄物を排出するようにしたことを特徴とするものである。   The configuration of the processing apparatus of the present invention, which has been made for the purpose of solving the above-mentioned problems, hydrolyzes and carbonizes organic waste in a pressure-resistant container while stirring it in a high-temperature and high-pressure environment. A waste processing apparatus for processing, a steam supply means for supplying high-temperature saturated steam into the container, a temperature adjusting means for adjusting the temperature in the container, and a pressure in the container Pressure adjusting means for adjusting by an on-off valve, steam discharging means for forcibly discharging water vapor generated in the container, and a shaft penetrating the container to stir the charged waste in the container. Provided with a stirring means, the temperature in the container is adjusted to 220 to 260 ° C. by the temperature adjusting means, the pressure in the container is adjusted to 2 to 3 MPa by the pressure adjusting means, and high temperature is generated by the steam supply means. By supplying saturated water vapor and stirring the organic waste, the treatment is performed by drying the water vapor while forcibly discharging the water vapor in the container, and after the treatment, The treated organic waste is discharged by adjusting the pressure below atmospheric pressure.

また、本発明は、上記構成において、前記撹拌手段において、スクリュウ羽根が前記撹拌するための前記軸に設けられる、或いは前記スクリュウ羽根は、20〜40回転/分で、正逆回転させながら使用する、或いは更に、前記処理における乾燥を促すための第1乾燥手段を備える、或いは前記処理の後、前記圧力調整手段により前記容器内の圧力を大気圧以下に調節した場合において、該調節の後に前記処理された前記有機系廃棄物を乾燥させるための第2乾燥手段を更に備える構成にすることができる。   Further, in the above-described configuration, the present invention is configured such that, in the stirring means, a screw blade is provided on the shaft for stirring, or the screw blade is used while being rotated forward and backward at 20 to 40 rotations / minute. Or further comprising a first drying means for promoting drying in the treatment, or after the treatment, when the pressure in the container is adjusted to an atmospheric pressure or lower by the pressure adjusting means, after the adjustment, It can be set as the structure further equipped with the 2nd drying means for drying the processed said organic waste.

本発明装置で処理する有機系廃棄物としては、使用済みの敷き藁、および/または、医療廃棄物、または、肉、野菜、魚の残渣や売れ残りの弁当などの生ゴミ、または、包装紙、段ボール、プラスチック製の容器や袋、ペットボトル、発泡スチロールなどのプラスチック類、もしくは、木材片や伐採された樹木、草など、或いは、医療廃棄物、もしくは、汚泥または畜産廃棄物などが挙げられる。   Organic waste to be treated by the apparatus of the present invention includes used litter and / or medical waste, meat such as vegetables, fish residues and unsold lunches, wrapping paper, cardboard And plastics such as plastic containers and bags, plastic bottles, polystyrene foam, wood pieces, felled trees, grasses, medical waste, sludge or livestock waste.

ここで、本発明に係る装置の処理原理について説明すると、本発明装置は、高温・高圧滅菌装置であるが、処理対象を有機系廃棄物のうち敷き藁や医療廃棄物など分解し易いものに限定しその無菌化・無害化処理をするので、超臨界水条件下での処理は必要なく、亜臨界水条件下での水熱反応で充分である。処理に当たっては装置内に飽和水蒸気を供給することで、亜臨界条件下で処理を行なう。即ち、高温・高圧水中での処理となる。一般に、水は高い解離度と大きな誘電率を持つことが特徴であるが、常温の水では、水素イオンの濃度によって酸性やアルカリ性といった性質が発現する。また、水自身の水素イオンと水酸化物イオンがそれぞれ反応して物質を分解する反応は加水分解として知られている。無機化合物でも有機化合物でも酸素を挟んだ結合、有機化合物ではエステルやエーテル結合、無機化合物では酸化物は、水によって相互に水酸化物を橋にして分解する。   Here, the processing principle of the apparatus according to the present invention will be described. The apparatus of the present invention is a high-temperature / high-pressure sterilization apparatus, but the processing target is made of organic waste such as litter and medical waste that can be easily decomposed. Since it is limited and sterilized and detoxified, treatment under supercritical water conditions is not necessary, and hydrothermal reaction under subcritical water conditions is sufficient. In the process, the process is performed under subcritical conditions by supplying saturated water vapor into the apparatus. That is, the treatment is performed in high temperature / high pressure water. In general, water is characterized by a high degree of dissociation and a large dielectric constant, but water at normal temperature exhibits properties such as acidity and alkalinity depending on the concentration of hydrogen ions. A reaction in which hydrogen ions and hydroxide ions of water itself react to decompose a substance is known as hydrolysis. Bonds sandwiching oxygen in both inorganic and organic compounds, ester and ether bonds in organic compounds, and oxides in inorganic compounds are decomposed by water with hydroxides as bridges.

また、高温・高圧の状態では、水の解離度は温度の上昇とともに進行し250℃付近で最大に達してから下降する。これは温度の変化によって水の酸或いはアルカリとしての性質も大きく影響を受けることを意味する。即ち、亜臨界の飽和蒸気圧下では、水の解離度が大きいため、酸・アルカリの性質が強く、反応活性な溶媒となる。従って、亜臨界水中では反応活性な水分子による加水分解反応が起こり、300℃前後で最も反応が激しくなる。   In a high temperature / high pressure state, the degree of water dissociation proceeds with increasing temperature, reaches a maximum at around 250 ° C., and then decreases. This means that the properties of water as an acid or alkali are greatly affected by changes in temperature. That is, under the subcritical saturation vapor pressure, the dissociation degree of water is large, so that the acid / alkali property is strong and the reaction active solvent is obtained. Therefore, in subcritical water, a hydrolysis reaction occurs due to reactive water molecules, and the reaction becomes most intense at around 300 ° C.

また、飽和蒸気圧下ということは気相と液相が混在している状態なので、液相では加水分解反応が、気相では脱水縮合反応が優先する。一般に、亜臨界の飽和蒸気圧下における液相中ではイオン反応や加水分解反応の加速化、気相中ではラジカル反応が優先するとされている。このような亜臨界水や超臨界水での反応は水熱反応として知られている。   In addition, since the saturated vapor pressure is a state in which the gas phase and the liquid phase are mixed, priority is given to the hydrolysis reaction in the liquid phase and the dehydration condensation reaction in the gas phase. In general, it is said that acceleration of ion reaction and hydrolysis reaction is prioritized in the liquid phase under subcritical saturation vapor pressure, and radical reaction is prioritized in the gas phase. Such a reaction with subcritical water or supercritical water is known as a hydrothermal reaction.

本発明装置は、上記の通り、亜臨界の飽和蒸気圧下における水熱反応を利用しており、処理前に内部空気の排出を行なわない。そのため処理は酸素の存在下で行なわれるが、220℃程度の低温域では酸素の存在によって酸化反応を伴う。酸化反応は電子を奪う反応であるが、一般に水を媒介とした場合には電子の授受がより容易となる。このような水熱条件のもとでの酸化反応は水熱酸化反応として知られている。   As described above, the apparatus of the present invention utilizes a hydrothermal reaction under a subcritical saturated vapor pressure and does not discharge internal air before the treatment. Therefore, the treatment is performed in the presence of oxygen, but in the low temperature range of about 220 ° C., an oxidation reaction is accompanied by the presence of oxygen. Although the oxidation reaction takes away electrons, generally, when water is used as a medium, it is easier to exchange electrons. Such an oxidation reaction under hydrothermal conditions is known as a hydrothermal oxidation reaction.

本発明装置は、有機系廃棄物のうち、分解され易い、敷き藁や医療廃棄物を主な処理対象としているが、廃プラスチックなども処理することができる。主な廃プラスチックであるポリオレフィン、ポリスチレン、ポリ塩化ビニルは一般に温度に依存した熱分解性を示す。しかし、これらのプラスチックの熱安定性はポリ塩化ビニル、ポリスチレン、ポリオレフィンの順で強くなることで知られ、真空中の揮発率は200℃程度ではきわめて低いことが知られており、本発明装置における処理に当たっても熱分解の寄与は低いと考えられる。本発明装置では、220℃の亜臨界水条件下で上述のように亜臨界水での反応機構から液相中では加水分解反応やイオン反応、気相中では脱水縮合反応やラジカル反応、熱分解および水熱酸化により廃プラスチックが分解されるものと推定される。また、処理残渣は未分解の廃プラスチックと推定される。このような分解物は蒸気とともに本発明装置内から排出され、サイクロンを経由して粉塵等が分離され、残りの蒸気はエジェクタで冷却水との気液接触によりその大部分は冷却液化し、微生物処理および活性炭によって廃水処理される。また、余剰ガス中の未分解物は二次処理されて排出される。   The apparatus according to the present invention mainly deals with litter and medical waste that are easily decomposed among organic wastes, but can also treat waste plastics and the like. Major waste plastics such as polyolefin, polystyrene, and polyvinyl chloride generally exhibit temperature-dependent thermal decomposability. However, the thermal stability of these plastics is known to increase in the order of polyvinyl chloride, polystyrene, and polyolefin, and the volatility in vacuum is known to be extremely low at about 200 ° C. Even in the treatment, the thermal decomposition is considered to contribute little. In the apparatus of the present invention, hydrolysis reaction and ion reaction in the liquid phase, dehydration condensation reaction, radical reaction, thermal decomposition in the gas phase from the reaction mechanism in subcritical water as described above under the subcritical water condition at 220 ° C. It is estimated that waste plastics are decomposed by hydrothermal oxidation. Moreover, a processing residue is estimated to be undecomposed waste plastic. Such decomposition products are discharged from the apparatus of the present invention together with steam, dust and the like are separated through a cyclone, and most of the remaining steam is cooled and liquefied by gas-liquid contact with cooling water by an ejector, and microorganisms Treatment and wastewater treatment with activated carbon. In addition, undecomposed matter in the surplus gas is subjected to secondary treatment and discharged.

本発明装置は、有機系廃棄物のうち、分解され易い、敷き藁や医療廃棄物を主な処理対象とし、亜臨界水条件下での水熱反応を利用しているので、装置の製作が容易であるという効果がある。また、本発明装置は敷き藁に繁殖している微生物や雑菌、医療廃棄物に付着している病原菌を水蒸気による高温・高圧条件下の水熱酸化反応により滅菌、死滅させることができるので、従来、消毒や殺菌処理等を施してからでなければ処理できなかった廃棄物を容易に処理できるという格別の効果が得られる。   The device of the present invention is mainly used for organic waste, such as litter and medical waste, which is easily decomposed, and uses hydrothermal reaction under subcritical water conditions. There is an effect that it is easy. In addition, since the device of the present invention can sterilize and kill microorganisms and other germs that are propagated on the litter by a hydrothermal oxidation reaction under high temperature and high pressure conditions using water vapor, In addition, it is possible to obtain a special effect that waste that can only be treated after disinfection or sterilization treatment can be easily treated.

また、本発明装置は密閉された容器内で分解等の処理を行なうため、生ゴミや畜産廃棄物などであっても処理中に悪臭を外部に発散させることがないという効果が得られる。   In addition, since the apparatus of the present invention performs processing such as decomposition in a sealed container, an effect is obtained that odors are not diffused to the outside even during processing, such as garbage and livestock waste.

本発明の一例の有機系廃棄物処理装置の断面図である。It is sectional drawing of the organic waste processing apparatus of an example of this invention.

本発明の実施形態について、図を用いて説明する。図1は本発明の一例の有機系廃棄物処理装置の断面図である。図1において、1は耐熱耐圧容器で、ここでは内部温度600℃、内部圧力5MPa程度に耐え得る容器を用いている。2はこの容器1内に有機系廃棄物を投入するための廃棄物投入口、3は耐熱耐圧容器1の機密性を保持しつつ廃棄物投入口2に投入する有機系廃棄物を貯留しこの容器1内に投入する装置である。4は廃棄物処理後の炭化物等の取出口、5は耐熱耐圧容器1の機密性を保持しつつ取出口4から取出した炭化物等を一旦貯留する処理済貯留部である。   Embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a cross-sectional view of an organic waste treatment apparatus according to an example of the present invention. In FIG. 1, reference numeral 1 denotes a heat-resistant pressure-resistant container, which is a container that can withstand an internal temperature of 600 ° C. and an internal pressure of about 5 MPa. Reference numeral 2 denotes a waste input port for supplying organic waste into the container 1, and 3 denotes an organic waste to be input to the waste input port 2 while maintaining the confidentiality of the heat and pressure resistant container 1. It is a device that is put into the container 1. Reference numeral 4 denotes an outlet for the carbide after the waste treatment, and reference numeral 5 denotes a processed storage section for temporarily storing the carbide extracted from the outlet 4 while maintaining the confidentiality of the heat and pressure resistant container 1.

ちなみに、耐熱耐圧容器1については、内部温度600℃、内部圧力5MPaに耐え得るようにすれば、材質は問わず、そして当該容器の層構造は、単構造や二重構造等適宜採用すればよい。また、廃棄物投入口2、廃棄物投入装置3、取出口4、処理済貯留部5については、形状等特に限定はない。   Incidentally, the heat and pressure resistant container 1 may be of any material as long as it can withstand an internal temperature of 600 ° C. and an internal pressure of 5 MPa, and the layer structure of the container may adopt a single structure or a double structure as appropriate. . Further, the shape of the waste input port 2, the waste input device 3, the outlet 4, and the treated storage portion 5 is not particularly limited.

6は耐熱耐圧容器1内に設けられている攪拌手段としてのスクリュウ羽根であり、この容器1内に貫通して設けられている軸7に取り付けられ、モータ8によって回転させられる。耐熱耐圧容器1内に投入された廃棄物は、このスクリュウ羽根6によって攪拌されると共に、モータ8の正逆回転制御によってこの容器1内を前後に移動させられるようになっている。ちなみに、スクリュウ羽根6の羽根形状やモータ8については、特に限定はない。   Reference numeral 6 denotes a screw blade as stirring means provided in the heat and pressure resistant container 1, which is attached to a shaft 7 provided penetrating in the container 1 and rotated by a motor 8. The waste thrown into the heat and pressure resistant container 1 is agitated by the screw blades 6 and can be moved back and forth in the container 1 by forward / reverse rotation control of the motor 8. Incidentally, the blade shape of the screw blade 6 and the motor 8 are not particularly limited.

9は水蒸気供給装置で、ここで発生した高熱の飽和水蒸気を供給管9aにより耐熱耐圧容器1内に供給する。10は圧力調整装置で、接続管10aにより耐熱耐圧容器1に接続し、この容器1内の圧力を開閉弁(図示せず)により調節して所定の圧力に調整する。なお、開閉弁については、手動開閉でも自動開閉でもよく、自動開閉の場合は、後述の中央制御装置17に連通や無線等の配線でも任意の方法を採れば良い。   Reference numeral 9 denotes a steam supply device, which supplies the high-temperature saturated steam generated here into the heat-resistant pressure-resistant container 1 through the supply pipe 9a. A pressure adjusting device 10 is connected to the heat and pressure resistant container 1 by a connecting pipe 10a, and the pressure in the container 1 is adjusted by an on-off valve (not shown) to be adjusted to a predetermined pressure. Note that the on / off valve may be manually opened or closed, and in the case of automatic opening / closing, any method may be employed for communication with the central control device 17 described later or wiring by radio.

11は耐熱耐圧容器1内の温度を所望の温度に調整するための温度調節装置で、ここでは耐熱耐圧容器1の外側に加熱コイル11aを巻回すように設け、この加熱コイル11aへの通電を制御することによりこの容器1内の温度を制御している。なお、耐熱耐圧容器1内の温度調整は、加熱コイル11aによるほか、ガスによる燃焼加熱によることもある。   Reference numeral 11 denotes a temperature adjusting device for adjusting the temperature in the heat and pressure resistant container 1 to a desired temperature. Here, a heating coil 11a is provided around the heat resistant and pressure resistant container 1 so as to energize the heating coil 11a. By controlling, the temperature in the container 1 is controlled. The temperature adjustment in the heat and pressure resistant container 1 may be performed by combustion heating with gas in addition to the heating coil 11a.

12はサイクロンで、開閉弁12aを介して耐熱耐圧容器1に接続し、有機系廃棄物の分解により発生した余剰ガスを取出して粉塵等を分離し、残りのガスや蒸気をエジェクタ13において冷却水との気液接触によりその大部分を冷却液化し、微生物処理および活性炭によって廃水処理する。14は耐熱耐圧容器1内の水蒸気を強制的に排出する強制排出装置である。   A cyclone 12 is connected to the heat-resistant pressure-resistant container 1 via the on-off valve 12a, takes out surplus gas generated by the decomposition of the organic waste, separates dust and the like, and the remaining gas and steam are cooled in the ejector 13 with cooling water. Most of the liquid is cooled and liquefied by gas-liquid contact with microbial treatment, and wastewater is treated with activated carbon. Reference numeral 14 denotes a forced discharge device for forcibly discharging water vapor in the heat and pressure resistant container 1.

15は圧力センサ、16は温度センサで、これらによって耐熱耐圧容器1内の圧力と温度を有機系廃棄物の処理中に監視する。17は中央制御装置で、これらの圧力センサ15、温度センサ16による圧力と温度の測定結果に基づき、制御信号ケーブルにより、耐熱耐圧容器1に設けられたすべての装置、即ち、廃棄物投入口2に設けられた有機系廃棄物の貯留投入装置3、取出口4に設けられた廃棄物の処理済貯留部5、スクリュウ羽根6を回転させるモータ8、耐熱耐圧容器1内に高熱の飽和水蒸気を供給する水蒸気供給装置9、耐熱耐圧容器1内の圧力を調整する圧力調整装置10、耐熱耐圧容器1内の温度を調節する温度調節装置11、開閉弁12a、乾燥時に発生する水蒸気を耐熱耐圧容器1の外に排出するための強制排出装置14の作動を制御する。   A pressure sensor 15 and a temperature sensor 16 monitor the pressure and temperature in the heat and pressure resistant container 1 during the treatment of the organic waste. Reference numeral 17 denotes a central control unit. Based on the pressure and temperature measurement results of the pressure sensor 15 and the temperature sensor 16, all devices provided in the heat-resistant pressure-resistant container 1 by the control signal cable, that is, the waste inlet 2 The organic waste storage and input device 3 provided in the container, the waste storage and storage unit 5 provided in the outlet 4, the motor 8 for rotating the screw blades 6, and the hot heat and pressure resistant container 1 are filled with high-temperature saturated steam. A steam supply device 9 for supplying, a pressure adjusting device 10 for adjusting the pressure in the heat and pressure resistant container 1, a temperature adjusting device 11 for adjusting the temperature in the heat and pressure resistant container 1, an on-off valve 12a, and a water pressure and pressure resistant container for generating steam during drying. 1 to control the operation of the forced discharge device 14 for discharging to the outside.

本発明装置では、中央制御装置17で上記の各装置の作動を制御しながら、耐熱耐圧容器1内の温度を220〜260℃、圧力を2〜3MPaに調節し、上記スクリュウ羽根6を回転させて有機系廃棄物をこの容器1内で攪拌することにより乾燥させて有機系廃棄物を加水分解すると共に、熱分解し、炭化して処理する。なお、乾燥時には強制排出装置14により発生する水蒸気を耐熱耐圧容器1外に放出するが、圧力調整装置10により容器1内の圧力が2〜3MPaより低くならないようにする。圧力が2〜3MPa以内でないと、加水分解、熱分解および炭化処理といった処理がうまくいかないからである。   In the device of the present invention, the temperature in the heat and pressure vessel 1 is adjusted to 220 to 260 ° C. and the pressure is adjusted to 2 to 3 MPa while controlling the operation of each device by the central control device 17, and the screw blade 6 is rotated. Then, the organic waste is dried by stirring in the container 1 to hydrolyze the organic waste, and is thermally decomposed and carbonized for treatment. In addition, although the water vapor | steam generate | occur | produced by the forced discharge apparatus 14 is discharge | released out of the heat-resistant pressure-resistant container 1 at the time of drying, the pressure inside the container 1 is made not to become lower than 2-3 MPa by the pressure regulator 10. If the pressure is not within 2 to 3 MPa, treatments such as hydrolysis, thermal decomposition and carbonization will not be successful.

ちなみに、当該処理におけるスクリュウ羽根6を用いた撹拌については、回転速度を20〜40回転/分で、かつ正逆回転が望ましい。正逆回転を採用する理由としては、当該廃棄物の処理を万遍なくいきわたらせるためである。また、回転速度を20〜40回転/分とする理由としては、20回転/分未満であると、当該処理が十分にいかず、40回転/分よりも大きくしてもさほど処理効率が上がるわけではない。   Incidentally, about the stirring using the screw blade 6 in the said process, a rotational speed is 20-40 rotation / min and forward / reverse rotation is desirable. The reason for adopting the forward / reverse rotation is to distribute the wastes uniformly. Moreover, as a reason for setting the rotation speed to 20 to 40 rotations / minute, if the rotation speed is less than 20 rotations / minute, the processing is not sufficiently performed, and even if the rotation speed is higher than 40 rotations / minute, the processing efficiency is increased. is not.

そして、当該処理における乾燥については、スクリュウ羽根6による撹拌だけで十分に成立する。しかしながら、廃棄物によっては、含水率が高く、熱分解や炭化処理が十分に成されない可能性がある。その乾燥を促進させるための乾燥手段(図示せず。以下これを「第1乾燥手段」という。)を設けても良い。第1乾燥手段については、使用時に耐熱耐圧容器1内の設定温度や圧力(220〜260℃、2〜3MPa程度)を変化させない程度であれば、乾燥方法については適宜種々の方法(例えば連続的もしくは断続的な乾燥用ガスのフロー)を採用でき、また乾燥に用いるガスについては、空気もしくは窒素等の不活性ガスを用いればよい。また第1乾燥手段の設置は耐熱耐圧容器1に直付けしても、配管を介すなど任意の手段を採用可能であり、第1乾燥手段の使用もしくは不使用を速やかにできるように開閉弁や開閉コックなどの任意の開閉手段を、第1乾燥手段および耐熱耐圧容器1の間に設ければよい。また、第1乾燥手段および該開閉手段等は中央制御装置17に連結して用いても、連結させずに独立させて用いても良い。   And the drying in the said process is fully established only by stirring with the screw blade 6. However, depending on the waste, the moisture content is high, and there is a possibility that thermal decomposition and carbonization are not sufficiently performed. A drying means (not shown, hereinafter referred to as “first drying means”) for promoting the drying may be provided. About the 1st drying means, if it is a grade which does not change the set temperature and pressure (220-260 degreeC, about 2-3 MPa) in the heat-resistant pressure-resistant container 1 at the time of use, about drying methods, various methods (for example, continuous) are suitably used. Alternatively, an intermittent drying gas flow) may be employed, and the gas used for drying may be air or an inert gas such as nitrogen. In addition, the first drying means can be installed directly on the heat-resistant pressure-resistant vessel 1, or any means such as through a pipe can be adopted. The on-off valve can be used promptly to use or not use the first drying means. Any open / close means such as an open / close cock may be provided between the first drying means and the heat and pressure resistant container 1. The first drying means and the opening / closing means may be used by being connected to the central controller 17 or may be used independently without being connected.

耐熱耐圧容器1内の圧力は、有機系廃棄物の処理中に発生するガスによっても高くなるので、開閉弁12aの開閉を調節して余剰ガスを容器1外に取り出すことによっても圧力を調節する。取り出すに際しては、サイクロン12を経由して粉塵等を分離する。   Since the pressure in the heat and pressure resistant container 1 is increased by the gas generated during the treatment of the organic waste, the pressure is also adjusted by adjusting the opening / closing of the on-off valve 12a and taking out the excess gas outside the container 1. . When taking out, dust etc. are isolate | separated via the cyclone 12. As shown in FIG.

また、上記の圧力調節装置10によって、有機系廃棄物の処理後に残留物(廃棄物)を取出口4から処理済貯留部5に取り出すとき、この耐熱耐圧容器1内の圧力が大気圧以下になるように調節する。このようにしないと耐熱耐圧容器1内の水蒸気やガスが大気中に一気に放出されてしまい、微生物や病原菌が死滅しないで処理後の残留物に残っている場合はこれらも一緒に大気中に放出されてしまうからである。有機系廃棄物の処理後に残留物(廃棄物)を取出口4から処理済貯留部5に取り出す際、耐熱耐圧容器1の圧力調節、つまり大気圧以下に戻すだけでも本発明に係る装置は十分に成立する。この時点では廃棄物は炭化されており、原則水分は抜けているものと思われる。しかしながら、元々含水率が多い有機系廃棄物(例えば汚泥)を用いた場合、加水分解、熱分解および炭化といった処理を撹拌手段(および第1乾燥手段)で行ったとしても、処理済みの残留廃棄物の取り出しの際、該廃棄物の中にわずかに水分が残っている、もしくは臭気が残るといったことがあり得る。そこで更に該廃棄物を乾燥させるための乾燥手段(図示せず。上記第1乾燥手段とは別の手段であり、以下これを「第2乾燥手段」という。)を設けても良い。   In addition, when the residue (waste) is taken out from the outlet 4 to the treated reservoir 5 after the organic waste is processed by the pressure adjusting device 10, the pressure in the heat and pressure resistant container 1 is reduced to the atmospheric pressure or lower. Adjust so that If this is not done, water vapor and gas in the heat-resistant pressure-resistant container 1 will be released into the atmosphere at once, and if microorganisms and pathogens remain in the treated residue without being killed, they will also be released into the atmosphere together Because it will be done. When taking out the residue (waste) from the outlet 4 to the treated reservoir 5 after processing the organic waste, the apparatus according to the present invention is sufficient only by adjusting the pressure of the heat and pressure resistant container 1, that is, returning it to atmospheric pressure or less. Is established. At this point, the waste has been carbonized, and in principle it seems that moisture has been removed. However, when organic waste (eg, sludge) that originally has a high water content is used, even if treatments such as hydrolysis, thermal decomposition, and carbonization are performed by the stirring means (and the first drying means), the residual waste that has been treated. When removing an object, there may be a slight moisture remaining in the waste or an odor. Therefore, a drying means for drying the waste (not shown; a means different from the first drying means, hereinafter referred to as “second drying means”) may be provided.

第2乾燥手段については、公知の製品を用いても構わない。ちなみに、第2乾燥手段の設置場所については、取出口4と処理済貯留部5を連結している配管または処理済貯留部5に任意の配管を介して設置すればよい。そして、その配管に開閉弁や開閉コックなどといった開閉手段を設ける。なお該開閉手段は、自動方式でも手動方式でも構わないが、自動方式が望ましい。廃棄物の乾燥に関しては、前述のように加水分解、熱分解および炭化処理の後、耐熱耐圧容器1内の圧力を大気圧(1Pa)以下にした後に行う。   As the second drying means, a known product may be used. Incidentally, about the installation place of a 2nd drying means, what is necessary is just to install in the piping which connected the extraction port 4 and the processed storage part 5, or the processed storage part 5 via arbitrary piping. The piping is provided with opening / closing means such as an opening / closing valve and an opening / closing cock. The opening / closing means may be an automatic method or a manual method, but an automatic method is desirable. As described above, the drying of the waste is performed after the hydrolysis, thermal decomposition, and carbonization treatment, and after the pressure in the heat and pressure resistant container 1 is reduced to atmospheric pressure (1 Pa) or less.

なお、第2乾燥手段において、その乾燥には乾燥空気を用いる。乾燥空気の温度は凡そ100〜350℃くらいのものを指す。また乾燥空気の圧力は、0.1〜1MPaくらいが望ましい。その圧力が0.1MPa以下であると、廃棄物の含水率が下がらない。そして1MPa以上であっても設備投資の金額が増える割には、乾燥時間の短縮に効果が少ないことと、また耐熱耐圧容器1もしくは処理済貯留部5内で廃棄物の含水率は下がるものの、一般の廃棄物の加水分解性能は必ずしも改良されず、加水分解(熱分解および炭化処理も含む)処理廃棄物の再利用(例えば肥料や燃料)を考慮した場合に高温での劣化が心配されるため適切ではない。次に、乾燥空気の耐熱耐圧容器1もしくは処理済貯留部5内での保持(維持)時間であるが、1分〜5分が望ましい。その保持(維持)時間が1分以下であると、乾燥空気の圧力が安定しない。また、その保持(維持)時間が5分以上であると、乾燥空気の圧力は安定しても、乾燥の効率はさほど上がらない。   In the second drying means, dry air is used for the drying. The temperature of the dry air is about 100 to 350 ° C. The pressure of dry air is preferably about 0.1 to 1 MPa. When the pressure is 0.1 MPa or less, the moisture content of the waste does not decrease. And although the amount of capital investment increases even if it is 1 MPa or more, although the effect of reducing the drying time is small, and the moisture content of the waste in the heat-resistant pressure-resistant container 1 or the treated storage part 5 decreases, Hydrolysis performance of general waste is not necessarily improved, and degradation at high temperatures is a concern when considering the reuse of hydrolyzed (including pyrolysis and carbonization) waste (eg fertilizer and fuel) Therefore it is not appropriate. Next, although it is holding (maintenance) time in the heat-resistant pressure-resistant container 1 or the processed storage part 5 of dry air, 1 minute-5 minutes are desirable. If the holding (maintaining) time is 1 minute or less, the pressure of the dry air is not stable. Further, when the holding (maintenance) time is 5 minutes or more, the drying efficiency does not increase so much even if the pressure of the drying air is stabilized.

温度調節装置11は、所望の圧力(2〜3MPa)において耐熱耐圧容器1内の温度を220℃以上(260℃程度まで)に調節するためのものであり、容器1内の温度が220℃より低くなったときは加熱コイル11aに通電して加熱するが、温度が高くなり過ぎたときは、水蒸気供給装置9からの高熱の飽和水蒸気の供給を制限したり、水蒸気を強制排出装置14により外部に放出するなどして調節する。   The temperature adjusting device 11 is for adjusting the temperature in the heat and pressure resistant container 1 to 220 ° C. or higher (up to about 260 ° C.) at a desired pressure (2 to 3 MPa). When the temperature is lowered, the heating coil 11a is energized and heated. However, when the temperature becomes too high, the supply of high-temperature saturated steam from the steam supply device 9 is restricted or the steam is forced to be externally discharged by the forced discharge device 14. Adjust it by releasing it.

以上、本発明装置に係る実施形態を述べたが、上記実施形態はあくまで一例であり、本発明に係る明細書、特許請求の範囲、図面に記載の事項の範囲を逸脱しなければ、種々の態様(形態)を採ることが可能である。   As mentioned above, although embodiment which concerns on this invention apparatus was described, the said embodiment is an example to the last, and if it does not deviate from the range of the matter described in the specification concerning this invention, a claim, and drawing, it will be various. It is possible to take an aspect (form).

上記に述べた実施形態につき、実施例を述べながら更に説明する。なお、下記実施例についてもまたあくまで一例であり、本発明に係る明細書、特許請求の範囲、図面に記載の事項の範囲を逸脱しなければ、種々の態様(形態)を採ることが可能であることを申し添える。また、必要に応じて、図1に記載の装置および符号を用いて説明する。   The embodiment described above will be further described with reference to examples. The following examples are also merely examples, and various modes (forms) can be adopted without departing from the scope of matters described in the specification, claims, and drawings of the present invention. I will tell you that there is. Moreover, it demonstrates using the apparatus and code | symbol as described in FIG. 1 as needed.

[実施例1]本発明装置により、実際に約3トンの微生物が繁殖している敷き藁を耐熱耐圧容器1内に投入し、容器1内の圧力を3MPa、温度を230℃にし、スクリュウ羽根6を1分間約36回転の速度で正逆回転させながら処理したところ、約30分間ですべて炭化処理することができた。また、取出口4から取り出した廃棄物の処理済貯留部5内の残留物を調べたところ、微生物や雑菌は全く検出されなかった。   [Embodiment 1] By using the apparatus of the present invention, a litter in which about 3 tons of microorganisms are actually propagated is put into a heat and pressure resistant container 1, the pressure in the container 1 is set to 3 MPa, the temperature is set to 230 ° C, and the screw blade 6 was processed while rotating in the forward and reverse directions at a speed of about 36 revolutions per minute, and all the carbonization could be performed in about 30 minutes. Moreover, when the residue in the processed storage part 5 of the waste taken out from the outlet 4 was examined, no microorganisms or germs were detected.

[実施例2]また、同様に、本発明装置を用い、回収業者から試験的に譲り受けた包帯や綿、シートなどの有機系医療廃棄物で、注射針などの無機物をも含む廃棄物を耐熱耐圧容器1内に投入し、容器1内の圧力を3MPa、温度を260℃にし、スクリュウ羽根6を1分間約36回転の速度で正逆回転させながら処理したところ、約40分間で、注射針を除き他のすべて炭化処理することができた。また、取出口4から取り出した廃棄物の処理済貯留部5内の残留物を調べたところ、病原菌は全く検出されず、また、残った注射針からも病原菌は検出されなかった。   [Example 2] Similarly, using the apparatus of the present invention, organic medical wastes such as bandages, cotton, sheets, etc. that have been handed over from a collector, heat-resistant waste containing inorganic substances such as injection needles, etc. When the pressure in the pressure vessel 1 is set, the pressure in the vessel 1 is 3 MPa, the temperature is 260 ° C., and the screw blade 6 is processed while rotating forward and backward at a speed of about 36 rotations for 1 minute, the injection needle takes about 40 minutes. Except for all other carbonization could be done. Moreover, when the residue in the processed storage part 5 of the waste taken out from the outlet 4 was examined, no pathogenic bacteria were detected, and no pathogenic bacteria were detected from the remaining injection needles.

[実施例3]更に、本発明装置で、肉、野菜、魚などの食品残渣や売れ残りの弁当などの生ゴミ類についても、また、包装紙や紙屑などの紙類についても、更に、段ボール、プラスチック製の容器や袋、ペットボトル、発泡スチロールなどのプラスチック類についても、それぞれ耐熱耐圧容器1内に投入して試験を行なったが、ほぼすべてを分解することができ、また、プラスチック類の場合は、メタン、エチレン、プロピレンといった燃焼性のガスや液体を燃料ガスや燃料油として回収することができた。   [Embodiment 3] Further, in the apparatus of the present invention, for food waste such as meat, vegetables and fish and unsold box lunches, and for paper such as wrapping paper and paper waste, cardboard, Plastics such as plastic containers, bags, plastic bottles, and polystyrene were also put in the heat and pressure resistant container 1 and tested, but almost all can be disassembled. Combustible gases and liquids such as methane, ethylene, and propylene were recovered as fuel gas and fuel oil.

[実施例4]また、本発明装置は、木材片や伐採された樹木、草などや汚泥や畜産廃棄物をも処理することができ、これらを容器1内の圧力を3MPa、温度を260℃にし、スクリュウ羽根6を1分間約36回転の速度で正逆回転させながら処理したところ、悪臭を発生することなく、大部分を分解等処理することができ、分解されないものにはダイオキシンなどの有害物質は全くないのでそのまま土壌に廃棄しても安全であることが確認できた。   [Embodiment 4] The apparatus of the present invention can also treat wood pieces, felled trees, grass, sludge, and livestock waste, and the pressure in the container 1 is 3 MPa and the temperature is 260 ° C. In addition, when the screw blades 6 were processed while rotating forward and backward at a speed of about 36 rotations per minute, most of them could be decomposed without generating bad odors. Since there was no substance at all, it was confirmed that it was safe to dispose of it directly in the soil.

本発明の有機系廃棄物の処理装置は、従来処分が難しいとされていた微生物や雑菌が繁殖した敷き藁や病原菌が付着した医療廃棄物を、これらの微生物や雑菌、病原菌を滅菌ないし殺菌すると同時に分解等して処分することができ、また、その他の生ゴミや畜産廃棄物、汚泥なども悪臭を発散することなく分解等して炭化処理することができるので、きわめて有用である。また、本発明装置は、廃プラスチック類も燃焼させずに分解等して処分することができるので、燃焼に伴うダイオキシンなどの有害物質を発生させることなく、安全な装置であるといえる。   The organic waste processing apparatus of the present invention sterilizes or sterilizes medical waste to which litter and pathogens that have been propagated with microorganisms and germs, which have been difficult to dispose of, are sterilized. It can be decomposed and disposed of at the same time, and other garbage, livestock waste, sludge and the like can be decomposed and carbonized without releasing bad odor, which is extremely useful. In addition, since the apparatus of the present invention can be disposed of by disassembling or disposing of waste plastics without burning, it can be said that the apparatus is safe without generating harmful substances such as dioxin accompanying combustion.

1 耐熱耐圧容器
2 廃棄物投入口
3 廃棄物投入装置
4 取出口
5 処理済貯留部
6 スクリュウ羽根
9 水蒸気供給装置
10 圧力調節装置
11 温度調節装置
11a 加熱コイル
12 サイクロン
12a 開閉弁
14 水蒸気の強制排出装置
15 圧力センサ
16 温度センサ
17 中央制御装置
DESCRIPTION OF SYMBOLS 1 Heat-resistant pressure-resistant container 2 Waste input port 3 Waste input device 4 Outlet 5 Processed storage part 6 Screw blade 9 Steam supply device 10 Pressure control device 11 Temperature control device 11a Heating coil 12 Cyclone 12a On-off valve 14 Forced discharge of water vapor Device 15 Pressure sensor 16 Temperature sensor 17 Central controller

Claims (8)

耐圧容器内において有機系廃棄物を高温・高圧の環境下で攪拌しながら加水分解すると共に、熱分解し、炭化して処理する廃棄物の処理装置であって、
前記容器内に高熱の飽和水蒸気を供給するための水蒸気供給手段と、
前記容器内の温度を調節するための温度調節手段と、
該容器内の圧力を開閉弁により調節する圧力調節手段と、
該容器内に生じる水蒸気を強制排出する水蒸気排出手段と、
投入された廃棄物を前記容器内で攪拌するため軸が当該容器内を貫通して設けられた攪拌手段を備え、
前記容器内の温度を前記温度調節手段により220〜260℃に調節し、前記容器内の圧力を前記圧力調節手段により2〜3MPaに調節し、前記水蒸気供給手段により高熱の飽和水蒸気を供給し、かつ前記有機系廃棄物を攪拌することにより、容器内の水蒸気を強制排出しながら乾燥させて前記処理をすると共に、該処理の後、前記圧力調整手段により前記容器内の圧力を大気圧以下に調節して、処理された前記有機系廃棄物を排出するようにしたことを特徴とする有機系廃棄物の処理装置。
A waste treatment apparatus that hydrolyzes and carbonizes and treats organic waste in a pressure vessel while stirring it in a high-temperature and high-pressure environment.
Water vapor supply means for supplying high-temperature saturated water vapor into the container;
Temperature adjusting means for adjusting the temperature in the container;
Pressure adjusting means for adjusting the pressure in the container by an on-off valve;
Water vapor discharging means for forcibly discharging water vapor generated in the container;
In order to stir the thrown-in waste in the container, the shaft includes a stirring means provided through the container,
The temperature in the container is adjusted to 220 to 260 ° C. by the temperature adjusting means, the pressure in the container is adjusted to 2 to 3 MPa by the pressure adjusting means, high-temperature saturated steam is supplied by the steam supply means, In addition, the organic waste is stirred to dry the water vapor in the container while forcibly discharging the water, and after the treatment, the pressure in the container is reduced to an atmospheric pressure or less by the pressure adjusting means. An organic waste processing apparatus characterized by adjusting and discharging the processed organic waste.
前記有機系廃棄物は、使用済み敷き藁である請求項1に記載の有機系廃棄物の処理装置。   The organic waste processing apparatus according to claim 1, wherein the organic waste is used litter. 前記有機系廃棄物は、医療廃棄物、肉、野菜もしくは魚などの食品残渣や売れ残りの弁当などの生ゴミ、包装紙や段ボールなどの紙類、プラスチック製の容器や袋、ペットボトル、発泡スチロールなどのプラスチック類、木材片や伐採された樹木、または草のいずれかである請求項1または2に記載の有機系廃棄物の処理装置。   The organic waste includes medical waste, food residue such as meat, vegetables or fish, raw garbage such as unsold lunches, paper such as wrapping paper and cardboard, plastic containers and bags, PET bottles, polystyrene foam, etc. The organic waste processing apparatus according to claim 1, wherein the apparatus is any one of plastics, wood pieces, felled trees, or grass. 前記有機系廃棄物は、汚泥または畜産廃棄物である請求項1ないし3のいずれか1項に記載の有機系廃棄物の処理装置。   The organic waste processing apparatus according to any one of claims 1 to 3, wherein the organic waste is sludge or livestock waste. 前記撹拌手段において、スクリュウ羽根が前記撹拌するための前記軸に設けられる請求項1ないし4のいずれか1項に記載の有機系廃棄物の処理装置。   The organic waste processing apparatus according to any one of claims 1 to 4, wherein in the stirring means, a screw blade is provided on the shaft for stirring. 前記スクリュウ羽根は、20〜40回転/分で、正逆回転させながら使用する請求項5に記載の有機系廃棄物の処理装置。   6. The organic waste treatment apparatus according to claim 5, wherein the screw blade is used while being rotated forward and reverse at 20 to 40 revolutions / minute. 更に、前記処理における乾燥を促すための第1乾燥手段を備える請求項1ないし6のいずれか1項に記載の有機系廃棄物の処理装置。   Furthermore, the organic waste processing apparatus of any one of Claim 1 thru | or 6 provided with the 1st drying means for promoting the drying in the said process. 前記処理の後、前記圧力調整手段により前記容器内の圧力を大気圧以下に調節した場合において、該調節の後に前記処理された前記有機系廃棄物を乾燥させるための第2乾燥手段を更に備え、該第2乾燥手段は、乾燥空気の圧力と、時間とをパルス変動させて該乾燥空気を供給する請求項1ないし7のいずれか1項に記載の有機系廃棄物の処理装置。
After the treatment, when the pressure in the container is adjusted to an atmospheric pressure or lower by the pressure adjustment means, the apparatus further comprises second drying means for drying the treated organic waste after the adjustment. The organic waste treatment apparatus according to any one of claims 1 to 7, wherein the second drying means supplies the dry air by changing the pressure and time of the dry air in pulses.
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