JP2006205027A - Apparatus and method for reducing volume/weight of hydrous organic sludge or the like - Google Patents
Apparatus and method for reducing volume/weight of hydrous organic sludge or the like Download PDFInfo
- Publication number
- JP2006205027A JP2006205027A JP2005019181A JP2005019181A JP2006205027A JP 2006205027 A JP2006205027 A JP 2006205027A JP 2005019181 A JP2005019181 A JP 2005019181A JP 2005019181 A JP2005019181 A JP 2005019181A JP 2006205027 A JP2006205027 A JP 2006205027A
- Authority
- JP
- Japan
- Prior art keywords
- hot air
- inner cylinder
- dryer
- dry distillation
- furnace
- 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
Images
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
- 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
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Coke Industry (AREA)
Abstract
Description
本発明は、有機汚泥や剪定枝、畜産廃棄物・食品廃棄物等の高水分含有産業廃棄物を乾燥し乾留を行い、発生する乾留ガスをエネルギーとして利用し、減量化並びに減容化を行い廃棄物の処理を行うとともに、有害なダイオキシン類を含むものに関しては、薬品により無害化し、製品として炭化物を取り出し、有用な資源として再利用する処理方法、並びに水分の多い有機汚泥を溶融する際に水蒸気爆発等の防止のための前処理方法及び処理装置に関する。 The present invention performs dry distillation by drying high moisture-containing industrial waste such as organic sludge, pruned branches, livestock waste, food waste, etc., and uses the generated dry distillation gas as energy to reduce and reduce the volume. In addition to treating waste and containing harmful dioxins, when detoxifying with chemicals, removing carbide as a product and reusing it as a useful resource, and melting organic sludge with a lot of moisture The present invention relates to a pretreatment method and a treatment apparatus for preventing a steam explosion or the like.
近年、環境問題に関する社会の関心が高まる中で、産業廃棄物として約70%を占める汚泥、並びに高水分含有廃棄物などを無害化処理し、且つ、より少ないエネルギーで資源化してリサイクルする技術開発が求められている。また、廃棄物等の埋立場の建設が付近住民の反対により出来ない状況が続き、埋立場の不足が問題化している。 In recent years, with increasing public interest in environmental issues, technology development has been made to detoxify sludge that occupies about 70% of industrial waste and waste containing high moisture, and to recycle it with less energy. Is required. In addition, the situation that the construction of landfills for waste, etc. cannot be done due to the opposition of the local residents, the shortage of landfills has become a problem.
特に汚泥に関しては、含まれる水分量が90%以上であるものが多く、廃棄物の重量のほとんどを占めている。
そのため、水分を分離し、廃棄物の重量を減少させることは重要である。従来は脱水機などを用いる場合が多いが、有機汚泥の場合には脱水直後の含水率はそれでも80%程度である。
完全に水分を分離するためには加熱蒸発が最も有効であるが、そのためには多量の化石燃料或いは電力が必要であり、多くのエネルギーを消費する。
また、近年一般的に用いられている溶融炉は、処理物に多量の水分が含まれていると水蒸気爆発や溶融不良の原因になる場合が多い。
従って、含水率の高い汚泥を溶融処理する場合には、脱水等の前処理が必要であり、含まれる有機物を有効に利用する手法が確立されていない。
乾留ガスを用いて、乾燥する方法は特開平8−253771号公報、特開平9−174031号公報、特開平9−210333号公報、特開平11−138133号公報で開示されているが、いずれも多量の含水率を持った有機汚泥等を乾燥乾留し、炭化物として回収する方法は提示されていない。
Especially for sludge, the amount of water contained is often 90% or more, and occupies most of the weight of waste.
Therefore, it is important to separate moisture and reduce the weight of waste. Conventionally, a dehydrator or the like is often used, but in the case of organic sludge, the water content immediately after dehydration is still about 80%.
Heat evaporation is most effective for completely separating water, but for that purpose, a large amount of fossil fuel or electric power is required, and a lot of energy is consumed.
In addition, melting furnaces that are generally used in recent years often cause a steam explosion or poor melting if a large amount of water is contained in the processed material.
Therefore, when the sludge having a high water content is melted, a pretreatment such as dehydration is required, and a method for effectively using the contained organic matter has not been established.
Methods for drying using dry distillation gas are disclosed in JP-A-8-253771, JP-A-9-174031, JP-A-9-210333, and JP-A-11-138133. No method has been proposed for drying and distilling organic sludge having a large water content and recovering it as carbides.
本発明は、上述のような技術的課題に鑑み、より少ない燃料で含水率の高い汚泥等の廃棄物を処理する装置及び方法であり、乾燥により発生する悪臭を乾留ガスとともに燃焼し、悪臭を分解する他、汚泥等の産業廃棄物を大幅に減容・減量することを目的とし、それはガス化溶融炉を含む溶融炉一般の原料の前処理にも利用できる。
また、乾燥乾留品は炭化物として鉄鋼業における還元剤等に使用が可能であり、廃棄物を処理するばかりでなく、リサイクル製品製造可能な技術の提供を目的とする。
さらに有害物を含んだ汚泥の場合、例えばダイオキシン類の分解薬剤と混合することにより、有害物は分解できる。
The present invention is an apparatus and method for treating waste such as sludge having a high water content with less fuel in view of the technical problems as described above, and burns malodor generated by drying together with dry distillation gas, In addition to decomposing, it aims to greatly reduce the volume of industrial waste such as sludge, and it can also be used for pretreatment of general raw materials for melting furnaces including gasification melting furnaces.
In addition, dry-distilled products can be used as reducing agents in the steel industry as carbides, and the purpose is not only to treat waste, but also to provide technology that can manufacture recycled products.
Furthermore, in the case of sludge containing harmful substances, the harmful substances can be decomposed, for example, by mixing with a dioxin decomposition agent.
特に、本発明は、多量に水を含んだ汚泥等を、最小のエネルギーの利用で減量し、同処理に係る経費を削減でき、且つ、不足する最終処分場の延命に貢献する技術である。 In particular, the present invention is a technology that can reduce sludge and the like containing a large amount of water by using a minimum amount of energy, reduce the cost of the treatment, and contribute to the extension of the shortage of final disposal sites.
上記目的を達成するために、本発明技術的要旨は、内筒と外筒からなる乾燥機の後工程に、内筒と外筒と、好ましくは中心筒からなる乾留炉を備え、乾留炉の内筒から発生した乾留ガスを燃焼させて熱風を発生させる熱風発生炉を備え、この熱風を乾燥機の内筒と外筒の間に導入する手段を備えたことを特徴とする。
より具体的には、回転円筒からなる内筒を備えた乾燥機並びに、回転円筒からなる内筒を備えた乾留炉を設備し、且つ乾留炉で発生した乾留ガスを、熱風発生炉で燃焼させ、熱量調整の目的で設置されたバーナー装置で混焼することにより発生した燃焼ガスにより、内筒に投入した汚泥を外熱方式で乾燥する点に特徴がある。
In order to achieve the above object, the technical gist of the present invention is to provide a dry distillation furnace consisting of an inner cylinder and an outer cylinder, preferably a central cylinder, in a subsequent process of a dryer consisting of an inner cylinder and an outer cylinder. A hot air generating furnace for generating hot air by burning dry distillation gas generated from the inner cylinder is provided, and means for introducing the hot air between the inner cylinder and the outer cylinder of the dryer is provided.
More specifically, a dryer equipped with an inner cylinder made of a rotating cylinder and a dry distillation furnace equipped with an inner cylinder made of a rotating cylinder are installed, and the carbonization gas generated in the carbonization furnace is burned in a hot air generating furnace. In addition, it is characterized in that the sludge thrown into the inner cylinder is dried by an external heating method by the combustion gas generated by co-firing with a burner device installed for the purpose of adjusting the amount of heat.
この場合に、有機汚泥等は連続的に系内に導入でき、回転円筒内に攪拌用の羽根を供えると、水分の蒸発効率の促進を図ることもできる。 In this case, organic sludge and the like can be continuously introduced into the system, and if a stirring blade is provided in the rotating cylinder, the evaporation efficiency of moisture can be promoted.
ここで、さらに熱風発生炉で発生させた熱風を、乾燥機の内筒と外筒の間を通過させた後に、さらに乾留炉の内筒と外筒の間に導入する手段を備えると、乾留炉の熱源として乾燥機の廃熱を利用できる。
また、廃熱をより有効に使用するために、中心筒にも熱風を通過させることも出来る。
その廃熱を利用した外熱式乾留炉へ乾燥した汚泥を導入するため、熱源と分離されており、灰分が少ない品質の良い炭化物を製造できる。
Here, after the hot air generated in the hot air generating furnace is further passed between the inner cylinder and the outer cylinder of the dryer, and further provided with means for introducing between the inner cylinder and the outer cylinder of the dry distillation furnace, The waste heat from the dryer can be used as a heat source for the furnace.
Moreover, in order to use waste heat more effectively, hot air can also be passed through the center tube.
Since the dried sludge is introduced into the external heating type carbonization furnace using the waste heat, it is separated from the heat source, and it is possible to produce a high quality carbide with less ash.
また、乾留ガスは有機汚泥等バイオ由来の原料が多いことから、その燃焼により発生する地球温暖化ガスとして問題視されている二酸化炭素はカーボンニュートラルの考え方により、地球上の二酸化炭素濃度の上昇の原因にはならない。
さらには、乾燥機の内筒から発生した乾燥後の排ガスを熱風発生炉に導入する手段を備えて、熱風発生炉にて再加熱利用するとエネルギーの有効利用がはかれる。
また、減容・減量装置を用いて、高含水有機汚泥を乾燥機で乾燥後に、乾留炉で乾留して炭化物を得ることができる。
有害物を含む原料の場合には、例えばダイオキシン類を含むものは、ダイオキシン類分解抑制薬剤を原料に混合することにより無害化が可能である。
Carbon dioxide, which is regarded as a problem as a global warming gas generated by combustion of carbon dioxide, is a problem of increasing the carbon dioxide concentration on the earth due to the concept of carbon neutral. It does not cause.
In addition, a means for introducing the exhaust gas after drying generated from the inner cylinder of the dryer into the hot air generating furnace is provided, and the energy can be effectively used when reheated in the hot air generating furnace.
Further, using a volume reduction / weight reduction device, the high water content organic sludge can be dried with a dryer and then carbonized in a carbonization furnace to obtain a carbide.
In the case of raw materials containing harmful substances, for example, those containing dioxins can be rendered harmless by mixing dioxins decomposition inhibiting agents with the raw materials.
本発明によれば、内筒と外筒からなる乾燥機の後工程に、内筒と外筒からなる乾留炉を備え、乾留炉の内筒から発生した乾留ガスを燃焼させて熱風を発生させる熱風発生炉を備え、この熱風を乾燥機の内筒と外筒の間に導入したので、ひとつの系内で、含水率の高い有機汚泥を非常に少ない燃料で乾燥し、乾留できる。
また、乾燥時に発生する悪臭は熱風発生炉にて燃焼分解され、外部に放出されることはない。
According to the present invention, a dry distillation furnace including an inner cylinder and an outer cylinder is provided in a subsequent process of a dryer including an inner cylinder and an outer cylinder, and hot air is generated by burning dry distillation gas generated from the inner cylinder of the dry distillation furnace. Since a hot air generating furnace is provided and this hot air is introduced between the inner cylinder and the outer cylinder of the dryer, organic sludge having a high water content can be dried with a very small amount of fuel and dry-distilled in one system.
Also, malodor generated during drying is combusted and decomposed in a hot air generating furnace and is not released to the outside.
以下、本発明の実施の形態による有機汚泥、剪定枝、畜産廃棄物、食品廃棄物、或いはその混合物の乾燥乾留処理システム及び処理方法(含水有機汚泥の減容・減量)を図1を参照して説明する。 Hereinafter, referring to FIG. 1, a dry-distillation treatment system and treatment method (volume reduction / reduction of water-containing organic sludge) of organic sludge, pruned branches, livestock waste, food waste, or a mixture thereof according to an embodiment of the present invention will be described. I will explain.
処理対象物である有機汚泥や剪定枝、畜産廃棄物、食品廃棄物等産業廃棄物は定量フィーダー3に投入する。投入方法は重機による手動投入方法でも、一旦、ホッパー等に有機汚泥や剪定枝、畜産廃棄物、食品廃棄物等産業廃棄物を仮保管し、一定量ずつ自動的にベルトコンベア或いはスクリューフィーダー等で定量フィーダー3に投入しても構わない。 Industrial waste such as organic sludge, pruned branches, livestock waste, food waste and the like to be treated is input to the quantitative feeder 3. The input method can be a manual input method using heavy machinery, or temporarily store organic sludge, pruned branches, livestock waste, food waste, or other industrial waste in a hopper, etc., and automatically by a belt conveyor or screw feeder. You may throw into the fixed_quantity | feed_rate feeder 3. FIG.
定量フィーダー3から乾燥機1内に一定量づつ原料は投入される。
有害物を含む有機汚泥等産業廃棄物を処理する場合、及びダイオキシン類の分解が必要な場合には、定量フィーダー3内で分解用薬剤と定量ずつ混合する。
A fixed amount of raw material is charged into the dryer 1 from the quantitative feeder 3.
When industrial waste such as organic sludge containing harmful substances is treated, or when decomposition of dioxins is necessary, it is mixed in a quantitative amount with a chemical for decomposition in a quantitative feeder 3.
乾燥機1は内筒(回転円筒)1aと外筒1bとで構成し、内筒と外筒の間に熱風を通過させることができる。
内筒は、回転円筒になっていて1°〜2°程度の傾斜角がつけられており、駆動モーターを動力とする回転によるすべりにより、有機汚泥や剪定枝、畜産廃棄物、食品廃棄物等産業廃棄物は回転円筒内を一定時間移動し、排出される。
回転円筒には汚染物をかきあげるリフター、あるいはパドル羽根が装着されていても良い。
The dryer 1 includes an inner cylinder (rotating cylinder) 1a and an outer cylinder 1b, and allows hot air to pass between the inner cylinder and the outer cylinder.
The inner cylinder is a rotating cylinder with an inclination angle of about 1 ° to 2 °, and organic sludge, pruned branches, livestock waste, food waste, etc. by sliding with rotation driven by a drive motor Industrial waste moves in the rotating cylinder for a certain time and is discharged.
The rotating cylinder may be equipped with a lifter for scavenging contaminants or paddle blades.
乾燥機1の内筒1aの外壁を覆うように外筒1bによる熱風の通過壁が設けられており、その熱が乾燥機1の回転円筒に伝わり、処理対象物である有機汚泥等の産業廃棄物を加熱する。 A hot air passage wall is provided by the outer cylinder 1b so as to cover the outer wall of the inner cylinder 1a of the dryer 1, and the heat is transferred to the rotating cylinder of the dryer 1 so that the industrial waste such as organic sludge that is the object to be treated is disposed. Heat the thing.
加熱源である熱風の温度は800℃以上であり、熱風発生炉6から供給される。熱風は乾燥機1の回転円筒の内側とは分離されており、乾燥時に発生するガスと混合することは無い。 The temperature of the hot air that is the heating source is 800 ° C. or higher, and is supplied from the hot air generator 6. The hot air is separated from the inside of the rotating cylinder of the dryer 1 and does not mix with the gas generated during drying.
乾燥機1の内筒と外筒との間を通過し、排出された熱風はおおむね500℃程度の温度を保ち、後述する乾留炉2の内筒(回転円筒)2aと外筒2bとの間に導入する。
また、乾留炉の内筒の内側に中心筒2cを設けた場合には、中心筒にも上記熱風を通す。
The hot air that has passed between the inner cylinder and the outer cylinder of the dryer 1 and that has been discharged maintains a temperature of about 500 ° C., and is between the inner cylinder (rotating cylinder) 2a and the outer cylinder 2b of the dry distillation furnace 2 described later. To introduce.
When the center tube 2c is provided inside the inner tube of the dry distillation furnace, the hot air is also passed through the center tube.
乾燥機1の回転円筒内を通過した乾燥処理物は乾燥機1から排出され、スクリューコンベア9で定量ずつ乾留炉2の回転円筒へ導入する。
乾留炉2の回転円筒には1°〜2°内の傾斜角がつけられており、回転によるすべりにより乾留炉2内回転円筒内を一定時間移動し、排出される。
回転円筒内には汚染物をかきあげるリフター、あるいはパドル羽根が装着されていても良い。
The dried processed product that has passed through the rotary cylinder of the dryer 1 is discharged from the dryer 1 and introduced into the rotary cylinder of the dry distillation furnace 2 by the
The rotating cylinder of the dry distillation furnace 2 is inclined at an angle of 1 ° to 2 °, and moves in the rotating cylinder in the dry distillation furnace 2 for a certain period of time by the sliding caused by rotation.
A lifter or paddle blade for scrubbing contaminants may be mounted in the rotating cylinder.
乾留炉2には、内筒2aの外壁を覆うように外筒2bを設け、かつ熱風の通過壁とし、また、内筒の内部に同じく熱風が通過する中心筒2cを配置した。
これにより、その熱が、処理対象物である乾燥した有機汚泥等産業廃棄物を加熱・乾留する。
In the dry distillation furnace 2, an outer cylinder 2b is provided so as to cover the outer wall of the inner cylinder 2a, and a hot-air passage wall is provided, and a central cylinder 2c through which the hot air similarly passes is disposed inside the inner cylinder.
Thereby, the heat heats and dry-distills industrial wastes, such as dried organic sludge which is a process target object.
乾留が終了し排出された炭化物はスクリューコンベア10で製品保管庫11へ搬送される。スクリューコンベア10は間接水冷されており、排出された製品を冷却する。なお、製品保管庫に至るまでに十分な冷却時間がある場合には、間接水冷は必要ない。
Carbide discharged after completion of dry distillation is transported to the
乾留炉2の内筒内を乾燥した原料が通過する際に発生する乾留ガスは、サイクロン20で微粉炭を除去し、熱風発生炉6に導入される。熱風発生炉6には熱量調整用のバーナー15が装着されており、重油サービスタンク7から供給される重油を油ポンプ8でバーナー15に供給している。
なお、サイクロン20は原料の性状により装備しなくとも良い。
温度調整は温度指示調節計16にて定量フィーダーへ投入する原料の投入量を制御し、乾燥機1内回転円筒内温度を管理する。
温度指示調節計19によりバーナー15を制御する。
The dry distillation gas generated when the dried raw material passes through the inner cylinder of the dry distillation furnace 2 removes pulverized coal with a
The
In the temperature adjustment, the
The
発生した熱風は乾燥機1の内筒1aと外筒1bとの間の熱風通過壁から乾留炉2の内筒2aと外筒2bの間の熱風通過壁及び中心筒2cをとおり、熱交換器12へ導入される。熱交換が行われた排ガスは乾留炉1の回転円筒内圧力を一定に保つために設置された圧力指示調節計17で制御され、排煙ファン13で吸引され、排突14から外気へ放出する。或いは、既設の排ガスダクトへ導入する。
The generated hot air passes from the hot air passage wall between the inner cylinder 1a and the outer cylinder 1b of the dryer 1 through the hot air passage wall between the inner cylinder 2a and the outer cylinder 2b of the dry distillation furnace 2 and the central cylinder 2c, and as a heat exchanger. 12 is introduced. The exhaust gas that has undergone heat exchange is controlled by a
炭化製品を製造する場合にも、乾留ガスを完全燃焼させるための特別な排ガス処理装置は不要である。
有害物質を含んだ有機汚泥、剪定枝、畜産廃棄物・食品廃棄物等を原料とする場合には、排ガス処理装置すなわち急速減温塔やバグフィルターを通過させる方が良い。
Even when producing a carbonized product, a special exhaust gas treatment device for completely burning dry distillation gas is not required.
When organic sludge containing toxic substances, pruned branches, livestock waste / food waste, etc. are used as raw materials, it is better to pass through an exhaust gas treatment device, that is, a rapid temperature reduction tower or a bag filter.
熱交換器12で熱交換された高温の空気は乾燥機1の回転円筒内1aに導入される。乾燥機1の熱風通過壁からの熱に加え、導入する高温空気により効率的に乾燥を行う。蒸発した水分とともに乾燥機1の回転円筒から排出され、サイクロン4で飛散した原料と分離する。
The high-temperature air heat-exchanged by the heat exchanger 12 is introduced into the rotating cylinder 1 a of the dryer 1. In addition to the heat from the hot air passage wall of the dryer 1, the drying is efficiently performed by the introduced high-temperature air. It is discharged from the rotating cylinder of the dryer 1 together with the evaporated water and separated from the raw material scattered by the
分離されたガスは排気ファン5で熱風発生炉に燃焼用空気として導入する。排気ファン5は温度指示調節計18により回転円筒の外筒温度を調節する。排気ファン5が送風するガスには多量の水分が含有しており、熱風発生炉から発生する熱風の酸素濃度は低く保持される。
The separated gas is introduced into the hot air generating furnace by the exhaust fan 5 as combustion air. The exhaust fan 5 adjusts the outer cylinder temperature of the rotating cylinder by a
なお、図1にて、TIC:温度コントロール、PIC:圧力コントロール、INV:インバーター制御を意味する。 In FIG. 1, TIC: temperature control, PIC: pressure control, INV: inverter control.
本発明に係る装置を試作し、水分量80kg/hからなる含水有機汚泥180kg/hを処理した結果、水分量0kg/hの製品(炭化物)8kg/hが得られた。
従って、原料は概ね4.4重量%まで減量したことになる。
A device according to the present invention was prototyped and treated with water-containing organic sludge of 180 kg / h having a water content of 80 kg / h. As a result, 8 kg / h of a product (carbide) having a water content of 0 kg / h was obtained.
Therefore, the raw material is reduced to approximately 4.4% by weight.
本発明の規模は概ね処理用として100kg/h〜10t/h程度に適用される。 The scale of the present invention is generally applied to about 100 kg / h to 10 t / h for processing.
1 (外熱式)乾燥機
1a 乾燥機の内筒(回転円筒)
1b 乾燥機の外筒
2 (外熱式)乾留炉
2a 乾留炉の内筒(回転円筒)
2b 乾留炉の外筒
2c 乾留炉の中心筒
3 定量フィーダー
4 サイクロン
5 排気ファン
6 熱風発生炉
7 重油タンク
8 重油ポンプ
9 スクリューコンベア
10 水冷式スクリューコンベア
11 製品タンク
12 熱交換器
13 排煙ファン
14 煙突
15 バーナー
16 温度指示調節計
17 圧力指示調節計
18 圧力指示調節計
19 温度指示調節計
20 サイクロン
1 (External heat type) dryer 1a Inner cylinder (rotating cylinder) of dryer
1b Dryer outer cylinder 2 (external heat type) carbonization furnace 2a Carbonization furnace inner cylinder (rotating cylinder)
2b Outer cylinder of dry distillation furnace 2c Central cylinder of dry distillation furnace 3
Claims (5)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2005019181A JP2006205027A (en) | 2005-01-27 | 2005-01-27 | Apparatus and method for reducing volume/weight of hydrous organic sludge or the like |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2005019181A JP2006205027A (en) | 2005-01-27 | 2005-01-27 | Apparatus and method for reducing volume/weight of hydrous organic sludge or the like |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2006205027A true JP2006205027A (en) | 2006-08-10 |
Family
ID=36962414
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2005019181A Pending JP2006205027A (en) | 2005-01-27 | 2005-01-27 | Apparatus and method for reducing volume/weight of hydrous organic sludge or the like |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2006205027A (en) |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100795347B1 (en) | 2007-04-30 | 2008-01-17 | 최송식 | Ejector, spin pipe dry unit, dry system having these for sludge and, drying method thereof |
JP2008056780A (en) * | 2006-08-30 | 2008-03-13 | Toshiba Corp | System for drying and carbonizing organic waste |
JP2008238129A (en) * | 2007-03-28 | 2008-10-09 | Japan Sewage Works Agency | Carbonization treatment equipment of sludge |
JP2009019156A (en) * | 2007-07-13 | 2009-01-29 | Victory:Kk | Carbonization-processing method |
CN103537477A (en) * | 2013-10-16 | 2014-01-29 | 华东理工大学 | Staged treatment equipment and technique for leather making wastes |
JP2016507374A (en) * | 2013-02-08 | 2016-03-10 | サック カンパニー リミテッド | Sludge treatment apparatus and method |
CN105757676A (en) * | 2016-03-01 | 2016-07-13 | 赵君华 | Garbage cracking furnace system |
JP2016217637A (en) * | 2015-05-21 | 2016-12-22 | 伊藤 鋼一 | Biomass fuel drying device |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001079510A (en) * | 1999-09-10 | 2001-03-27 | Kindai Setsubi Kk | Waste treating device |
JP2003262314A (en) * | 2002-03-08 | 2003-09-19 | Meidensha Corp | Heat treatment method and facility for water containing organic matter |
-
2005
- 2005-01-27 JP JP2005019181A patent/JP2006205027A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001079510A (en) * | 1999-09-10 | 2001-03-27 | Kindai Setsubi Kk | Waste treating device |
JP2003262314A (en) * | 2002-03-08 | 2003-09-19 | Meidensha Corp | Heat treatment method and facility for water containing organic matter |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008056780A (en) * | 2006-08-30 | 2008-03-13 | Toshiba Corp | System for drying and carbonizing organic waste |
JP2008238129A (en) * | 2007-03-28 | 2008-10-09 | Japan Sewage Works Agency | Carbonization treatment equipment of sludge |
KR100795347B1 (en) | 2007-04-30 | 2008-01-17 | 최송식 | Ejector, spin pipe dry unit, dry system having these for sludge and, drying method thereof |
JP2009019156A (en) * | 2007-07-13 | 2009-01-29 | Victory:Kk | Carbonization-processing method |
JP2016507374A (en) * | 2013-02-08 | 2016-03-10 | サック カンパニー リミテッド | Sludge treatment apparatus and method |
CN103537477A (en) * | 2013-10-16 | 2014-01-29 | 华东理工大学 | Staged treatment equipment and technique for leather making wastes |
JP2016217637A (en) * | 2015-05-21 | 2016-12-22 | 伊藤 鋼一 | Biomass fuel drying device |
CN105757676A (en) * | 2016-03-01 | 2016-07-13 | 赵君华 | Garbage cracking furnace system |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP5890440B2 (en) | Waste treatment method and apparatus | |
JP2006205027A (en) | Apparatus and method for reducing volume/weight of hydrous organic sludge or the like | |
KR100734092B1 (en) | Food waste treatment system using self-energy | |
JP2006266537A (en) | Waste treatment facility for treating refuse and sludge together | |
JP2008086982A (en) | Superheated steam continuously-recycling treatment apparatus | |
JP2008272720A (en) | Polluted soil treatment system using waste heat | |
JP2015224795A (en) | Generator for fuel gas from organic materials and utilization of heat of same | |
US7147681B1 (en) | Method and device for removing recoverable waste products and non-recoverable waste products | |
JP2011031226A (en) | Waste desalination method and waste desalination apparatus | |
JP4440696B2 (en) | Carbonization method of sewage sludge | |
JP5156253B2 (en) | Energy saving method by setting up industrial waste incineration facility in Ascon factory | |
KR100856677B1 (en) | Treatment apparatus of food rubbish | |
JP2005120210A (en) | Waste disposal by gasification and system therefor | |
JP2001327950A (en) | Incineration method and apparatus for solid waste | |
US11965651B2 (en) | Process for producing biomass by treatment of organic waste with two-step drying | |
JP4077811B2 (en) | Heat treatment equipment using superheated steam | |
JP2011068824A (en) | Carbonization facility for organic water-containing waste | |
JPS6152883B2 (en) | ||
WO2011014094A1 (en) | Method and device for recycling moist waste matter comprising organic materials | |
CN217763445U (en) | Industry is useless admittedly and mud processing system | |
KR100840910B1 (en) | Retreating apparatus of waste matters with high efficiency | |
US20230122230A1 (en) | Integrated plant for refuse incineration and for producing rock wool, and method for operating the plant | |
JP3769204B2 (en) | Combustion treatment method of waste including organic waste | |
JP2007284478A (en) | Method for converting bio-mass into resource and apparatus for conversion into resource | |
JP2009019156A (en) | Carbonization-processing method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20080117 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20100519 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20100614 |
|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20101019 |