JPH0480296A - Production of solid fuel from waste - Google Patents

Production of solid fuel from waste

Info

Publication number
JPH0480296A
JPH0480296A JP2193798A JP19379890A JPH0480296A JP H0480296 A JPH0480296 A JP H0480296A JP 2193798 A JP2193798 A JP 2193798A JP 19379890 A JP19379890 A JP 19379890A JP H0480296 A JPH0480296 A JP H0480296A
Authority
JP
Japan
Prior art keywords
waste
reaction
solid fuel
reactor
mixing
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP2193798A
Other languages
Japanese (ja)
Other versions
JP2954990B2 (en
Inventor
Tsuneo Azegami
畔上 統雄
Shozo Suzuki
鈴木 昭三
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
PLANDO KENKYUSHO KK
Original Assignee
PLANDO KENKYUSHO KK
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by PLANDO KENKYUSHO KK filed Critical PLANDO KENKYUSHO KK
Priority to JP2193798A priority Critical patent/JP2954990B2/en
Priority to PCT/JP1991/000961 priority patent/WO1992001771A1/en
Publication of JPH0480296A publication Critical patent/JPH0480296A/en
Application granted granted Critical
Publication of JP2954990B2 publication Critical patent/JP2954990B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • 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
    • Y02E50/10Biofuels, e.g. bio-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
    • 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

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Abstract

PURPOSE:To produce a solid fuel which is free from rotting, unpleasant odor and the danger of gas explosion, storable for a long period of time and excellent in combustibility by mixing and reacting a finely powdered waste and a quick lime-contg. additive material, degassing the reaction product, compression- molding it, and drying, neutralizing and sifting it. CONSTITUTION:A waste and an additive material containing an appropriate quantity of quick lime are charged into an agitated retention reactor. If desired, an appropriate quantity of an additive material comprising quick lime is further added. Then the charged materials are mixed and reacted and the gas formed by the reaction is removed to produce a secondarily formed waste. The latter is molded on a compression molding machine to give a tertiarily formed waste. The latter is dried and neutralized in a drying-neutralizing reactor and classified on a shifting machine to give a solid fuel. Thus, a solid fuel which is freed from rotting, storable for a long period of time, free from unpleasant odor and the danger of gas explosion, highly combustible and clean can be obtd.

Description

【発明の詳細な説明】 [発明の目的] (産業上の利用分野) この発明は、例えば一般家庭あるいは事業所なとから排
除されるこみなとの廃棄物を処理して、再度燃料として
使用できるようにする廃棄物による固形物燃料の製造方
法に関する。
[Detailed Description of the Invention] [Objective of the Invention] (Field of Industrial Application) This invention is a method for processing garbage and other wastes that are removed from, for example, ordinary households or businesses, so that they can be used again as fuel. The present invention relates to a method for producing solid fuel from waste.

(従来の技術) 従来、例えば一般家庭あるいは事業所などがら排除され
るこみなとの廃棄物は、近年益々増加傾向にあり、この
廃棄物を処分するのにどの工業化諸国においても頭を悩
ませているのが現状である。
(Prior art) The amount of waste that was traditionally disposed of in garbage, such as households or businesses, has been increasing in recent years, and disposing of this waste has been a problem for all industrialized countries. The current situation is that

そして、この廃棄物は、従来可燃性ごみと不燃性ごみに
大まかに区分され、可燃性ごみはごみ処理場に運搬され
て処分され、不燃性ごみは破砕されて可燃物、不燃物、
鉄類などに選別されるが、あるいはそのまま埋立地に運
搬されて埋立処分されているのである。いずれの場合に
おいても、汚染の危険性が高い。特に、焼却の場合、し
ばしば廃棄物中に含まれている有害物質或いは廃棄物の
燃焼過程で生ずる有害物質か排ガス処理装置て十分に除
去できず大気中に放出する可能性がある。
Conventionally, this waste is roughly classified into combustible waste and non-combustible waste, with combustible waste being transported to a garbage disposal site and disposed of, and non-combustible waste being shredded into combustible and non-combustible materials.
They are sorted into iron and other materials, or they are simply transported to a landfill and disposed of. In both cases there is a high risk of contamination. In particular, in the case of incineration, there is a possibility that harmful substances contained in the waste or harmful substances generated during the combustion process of the waste cannot be sufficiently removed by exhaust gas treatment equipment and may be released into the atmosphere.

したがって、こみなとの廃棄物の焼却処理に関しては、
非常に厳しい規制がある。
Therefore, regarding the incineration of garbage and waste,
There are very strict regulations.

そこで、廃棄物処理業者などは、上述したごとく単に廃
棄物を焼却したり、あるいは埋立地に処分するのでなく
、廃棄物を再利用できないか種々研究を重ねてきた結果
、廃棄物を処理して燃料として再利用すべく開発が行な
われている。
Therefore, as mentioned above, waste disposal companies have conducted various research into whether waste can be reused, instead of simply incinerating it or disposing of it in a landfill. Development is underway to reuse it as fuel.

すなわち、ごみなどの廃棄物における組成を調査してみ
ると、紙、ダンボール、繊維類が25〜45%、ゴム・
プラスチック類が7〜11%、厨芥その他の可燃物が7
〜18%、鉄類、アルミ。
In other words, when we investigate the composition of waste such as garbage, we find that paper, cardboard, and textiles account for 25 to 45%, while rubber and other materials account for 25% to 45%.
Plastics accounted for 7-11%, kitchen waste and other combustibles accounted for 7%.
~18%, iron and aluminum.

ガラス、土1石、複合物か5〜15%で、残りか水分と
なっていて、低位発熱量として2000〜2500 K
 c a !L/ k gを有している。
Glass, one stone of earth, and composites are 5 to 15%, and the rest is water, with a lower calorific value of 2000 to 2500 K.
ca! It has L/kg.

したがって、これらの廃棄物を処理して使用すれば充分
なエネルギーを有する燃料となることが知られているの
で、各国の関係機関によって、燃料として再利用すべく
開発が試みられている。
Therefore, it is known that if these wastes are processed and used, they can be turned into fuel with sufficient energy, and related organizations in various countries are attempting to develop them to reuse them as fuel.

(発明が解決しようとする課題) ところで、上述したごとく、従来の廃棄物を燃料として
再利用する手段を各機関か試みてきているか、未だ充分
に完成した固形物燃料ができていない。すなわち、ごみ
等の廃棄物を単に破砕して不燃物を取除く方法が用いら
れているが、腐敗物が完全に取除かれていないから、貯
蔵中に微生物によって分解し、長期の貯蔵かできないと
共に、悪臭、可燃性ガスが出てガス爆発を起こすなどの
問題が新たに生じたのである。これを避けるため、破砕
、選別した後、更に乾燥し、圧縮成型する方法も試みら
れているか、長期間の貯蔵中に吸湿し、同様な問題が生
してくる。また、廃棄物中に含まれるプラスチックを溶
融させるなどして強固なブリケットとする方法も試みら
れているが、燃焼性の悪い固形物燃料しか得られていな
い。さらに、基本的にごみ中には、燃焼性の窒素、揮発
性の塩素、硫黄などが含まれているため、これまではご
みからクリーンな燃料の製造がむずかしかった。
(Problems to be Solved by the Invention) As mentioned above, although various organizations have tried methods of reusing conventional waste as fuel, a fully developed solid fuel has not yet been produced. In other words, the method used is to simply crush garbage and other waste to remove non-combustible materials, but since putrefactive materials are not completely removed, they decompose by microorganisms during storage and can only be stored for a long time. At the same time, new problems arose, including bad odors, flammable gases, and gas explosions. In order to avoid this, methods have been tried in which the material is crushed and sorted, then further dried and compression molded, or else the material absorbs moisture during long-term storage, causing similar problems. In addition, attempts have been made to make strong briquettes by melting the plastic contained in the waste, but only solid fuel with poor combustibility has been obtained. Furthermore, garbage basically contains combustible nitrogen, volatile chlorine, sulfur, etc., so it has been difficult to produce clean fuel from garbage until now.

この発明の目的は、上記問題点を改善するため、腐敗性
を取除き、長期貯蔵ができ、しがち悪臭やガス爆発を起
さないようにすると共に、燃焼性がよく、クリーンな燃
料を得るようにした廃棄物による固形物燃料の製造方法
を提供することにある。
The purpose of this invention is to improve the above-mentioned problems by eliminating perishability, allowing long-term storage, preventing foul odors and gas explosions, and providing clean fuel with good combustibility. An object of the present invention is to provide a method for producing solid fuel from waste.

[発明の構成] (課題を解決するための手段) 上記目的を達成するために、この発明は、予め微粉砕さ
れた廃棄物と適宜な量のクイックライムを含んだ添加材
を混合貯留反応器に投入して混合・反応を行なった後、
反応された第1生成廃棄物を混合脱気反応器に投入し、
適宜な量のクイックライムを含んだ添加材を必要に応じ
て添加し、混合反応および反応生成ガスの脱気を行ない
、反応された第2生成廃棄物を圧縮成型機に投入して圧
縮成型を行ない、次いで、圧縮成型された第3生成廃棄
物を乾燥中和反応器に投入して乾燥中和反応を行ない、
さらに篩分器にて篩分して固形物燃料を得る廃棄物によ
る固形物燃料の製造方法である。
[Structure of the Invention] (Means for Solving the Problems) In order to achieve the above object, the present invention provides a storage reactor for mixing pre-pulverized waste and an additive material containing an appropriate amount of quick lime. After mixing and reacting,
Injecting the reacted first product waste into a mixed degassing reactor,
Add an appropriate amount of quicklime-containing additives as necessary, perform a mixing reaction and degas the reaction product gas, and then feed the reacted second product waste into a compression molding machine to perform compression molding. Then, the compression-molded third product waste is charged into a dry neutralization reactor to perform a dry neutralization reaction,
This is a method for producing solid fuel from waste which is further sieved using a sieve to obtain solid fuel.

また、前記製造方法において、前記混合貯留反応器にお
ける反応を密閉状態下、温度60’C以上100℃以下
で1時間以上行い、混合脱気反応器における反応を排気
状態下、前記温度より少くとも5℃以上高い温度で5分
間以上行うのが好ましい。
Further, in the manufacturing method, the reaction in the mixing storage reactor is carried out under a closed condition at a temperature of 60'C or more and 100°C or less for 1 hour or more, and the reaction in the mixing degassing reactor is carried out under an evacuated condition at least at a temperature lower than the above temperature. It is preferable to carry out the heating at a temperature higher than 5° C. for 5 minutes or more.

さらに、前記廃棄物による固形物燃料の製造方法におい
て、予め微粉砕された廃棄物とするために、廃棄物を第
1粗破砕機で破砕すると共に不燃物を選別除去し、次い
で第2粉砕機で破砕すると共に廃棄物の複合材中に含ま
れている不燃物を選別除去し、さらに、破砕された廃棄
物に適宜な量のクイックライムを含んだ添加材を投入し
、第3微粉砕機で破砕して微粉砕された廃棄物とするこ
と、さらに、前記反応された第1生成廃棄物、前記脱気
反応された第2生成廃棄物、あるいは前記篩分器にて篩
分された粉体の廃棄物を必要に応じてかつ、必要な量だ
け前記混合貯留反応器に還流することが望ましい。
Furthermore, in the method for producing solid fuel from waste, in order to obtain pulverized waste in advance, the waste is crushed in a first coarse crusher and noncombustible materials are sorted and removed, and then the waste is crushed in a second crusher. At the same time, incombustible materials contained in the waste composite material are separated and removed, and additives containing an appropriate amount of quick lime are added to the shredded waste, and the waste is crushed into a third pulverizer. to obtain finely pulverized waste, and further, the first product waste subjected to the reaction, the second product waste subjected to the deaeration reaction, or the powder sieved by the sieve divider. It is desirable to reflux the body waste to the mixing storage reactor as needed and in the required amount.

(作用) この発明の廃棄物による固形物燃料の製造方法を採用す
ることにより、予め微粉砕された廃棄物は、廃棄物を第
1粗破砕機で破砕すると共に不燃物を選別除去し、次い
で第2破砕機で破砕すると共に廃棄物の複合材中に含ま
れている不燃物を選別除去し、さらに、破砕された廃棄
物に適宜な量のクイックライムを含んだ添加材を投入し
、第3微粉砕機で破砕することによって、微粉砕された
廃棄物との間で混ぜられた微粉末な廃棄物か得られる。
(Function) By adopting the method of producing solid fuel from waste of this invention, the waste that has been pulverized in advance is crushed in the first coarse crusher, and non-combustible materials are sorted and removed. The waste is crushed in the second crusher, and the incombustible materials contained in the waste composite are sorted out, and an appropriate amount of additives containing quick lime are added to the crushed waste. 3 By crushing with a pulverizer, a finely powdered waste mixed with the finely pulverized waste is obtained.

こうして得られた微粉末な廃棄物と適宜な量のクイック
ライムを含んだ添加材の混合物を混合貯留反応器に投入
せしめることによって、廃棄物中の水分とクイックライ
ム(Cab)か反応してCa(OH)2となり、反応熱
によって温度が上昇しながら、Ca (OH)  と廃
棄物との反応か進み、貯留しながら混合して品質が均一
化した微粉末の第1生成廃棄物が得られる。この得られ
た第1生成廃棄物を混合脱気反応器に投入し、更に、適
宜な量のクイックライムを含んだ添加物を添加すると同
様な反応によって温度か上昇し、水蒸気とアンモニアを
含む反応ガスが発生するので、これを排除する。なお、
この段階では添加物を添加せず、反応器中に熱風を吹き
込むか、他の適当な方法によって廃棄物を加熱すること
によって反応ガスを発生させることもできる。このよう
にして得られた第2生成廃棄物を圧縮成型機に投入し、
粒状に成型された第3生成廃棄物を得る。次いで、第3
生成廃棄物を乾燥中和反応器に投入して乾燥せしめ、さ
らに篩分器にて篩分して固形物燃料が得られる。
By introducing a mixture of the fine powder waste obtained in this way and an additive material containing an appropriate amount of quick lime into a mixing storage reactor, the moisture in the waste reacts with quick lime (Cab) to produce Ca. (OH)2, and as the temperature rises due to the heat of reaction, the reaction between Ca (OH) and the waste proceeds, and by mixing while storing, the first generated waste is obtained as a fine powder with uniform quality. . When this obtained first product waste is put into a mixed degassing reactor and an appropriate amount of an additive containing quick lime is added, the temperature rises due to a similar reaction, and a reaction containing water vapor and ammonia occurs. Gas will be generated, so remove it. In addition,
No additives may be added at this stage, and the reaction gas may be generated by blowing hot air into the reactor or heating the waste by other suitable methods. The second generated waste thus obtained is put into a compression molding machine,
A third product waste product formed into granules is obtained. Then the third
The generated waste is put into a drying neutralization reactor, dried, and further sieved in a sieve to obtain solid fuel.

前記工程において、第2生成廃棄物、第3生成廃棄物、
あるいは篩分された粉体を必要に応じて、かつ必要な量
だけ前記混合貯留反応器に還流せしめることによって、
効率的な固形物燃料か得られる。
In the step, a second generated waste, a third generated waste,
Alternatively, by refluxing the sieved powder to the mixing storage reactor as needed and in the required amount,
Efficient solid fuel can be obtained.

(実施例) 以下、この発明の実施例を図面に基づいて詳細に説明す
る。
(Example) Hereinafter, an example of the present invention will be described in detail based on the drawings.

第1図を参照するに、例えば一般家庭あるいは事業所か
ら排除されるごみなどの廃棄物Wは、紙。
Referring to FIG. 1, waste W, such as garbage removed from households or businesses, is paper.

ダンボール、繊維類などの可燃物と、鉄、アルミガラス
、土1石なとの不燃物と、これらに含まれる水分なとて
構成されており、トラック、パッカー車などの運搬車な
とて運ばれてきて、−旦ホツバ−1に投入される。この
ホッパー1から必要な量だけ、必要な時期に第1粗破砕
機3に投入される。
It is composed of combustible materials such as cardboard and textiles, non-combustible materials such as iron, aluminum glass, and one stone of soil, and the moisture contained in these materials, and cannot be transported by transport vehicles such as trucks and packers. It is discovered and put into hotsuber 1. From this hopper 1, the required amount is fed into the first coarse crusher 3 at the required time.

第1粗破砕機3は例えば油圧低速駆動型の引裂き粗破砕
機で、具体的な構造は公知であるた・め、詳細な説明は
省略するか、回転数がそれぞれ異なる2又は3軸を有し
、各軸の外周にはそれぞれ複数の刃が備えられている。
The first coarse crusher 3 is, for example, a hydraulic low-speed driven tearing coarse crusher, and its specific structure is well known, so a detailed explanation will be omitted, or it may have two or three shafts with different rotational speeds. However, a plurality of blades are provided on the outer periphery of each shaft.

而して、投入された廃棄物を、回転数かそれぞれ異なる
2又は3軸の回転引裂刃によりくわえ込み、引裂き、強
固なものまで突き破って、低速、高トルクの油圧駆動に
よりゆっくり引裂かれ、本体下部の排出口から排出され
る。なお、この第1粗破砕機3の駆動は油圧駆動方式と
なっており、可変吐出アキシャルピストンポンプを使用
することにより、通常負荷時は、高速、低速トルクにて
、負荷増大時に低速、高速トルク運転と負荷の必要に応
して軸回転数を可変とすることができるため、破砕負荷
については、常時最適状態にて運転制御が可能となって
いる。
The input waste is gripped and torn by rotary tearing blades with two or three axes with different rotational speeds, breaking through even the strongest materials, and then being slowly torn apart by low-speed, high-torque hydraulic drive. It is discharged from the outlet at the bottom. The first coarse crusher 3 is driven by a hydraulic drive system, and by using a variable discharge axial piston pump, it operates at high speed and low speed torque under normal load, and at low speed and high speed torque when the load increases. Since the shaft rotation speed can be varied according to the needs of operation and load, it is possible to control the crushing load in an optimal state at all times.

この第1粗破砕機3で粗破砕された第1廃棄物WIは例
えばヘルドコンヘアなどからなる第1選別機5に送られ
る。この第1選別機5には磁選機か備えられていて、そ
の磁選機により鉄なとの金属が除去される。また、第1
選別機では、ビン。
The first waste WI coarsely crushed by the first coarse crusher 3 is sent to a first sorter 5 made of, for example, a held container. This first sorter 5 is equipped with a magnetic separator, and metals such as iron are removed by the magnetic separator. Also, the first
In the sorting machine, the bins.

ブロックなどの中粒形無機物が選別されて除去される。Medium-sized inorganic substances such as blocks are sorted out and removed.

第1選別機5で金属、無機物が除去されると、第1廃棄
物W1は第2粉砕機7に送られる。第2粉砕機7は例え
ばハンマミルなどからなっており、この第2粉砕機7て
廃棄物W1はさらに細かく粉砕される。
After metals and inorganic substances are removed by the first sorter 5, the first waste W1 is sent to the second crusher 7. The second crusher 7 includes, for example, a hammer mill, and the waste W1 is further finely crushed by the second crusher 7.

第2粉砕機7て細かく粉砕された第2廃棄物W2は例え
ば磁選機、篩分器、比重差分離機などからなる第2選別
機9に送られる。この第2選別機9ては、第1選別機5
て除去しきれなかった細かな金属や無機物か除去されて
、第3微粉砕機11に送られる。
The second waste W2 finely pulverized by the second pulverizer 7 is sent to a second sorter 9 comprising, for example, a magnetic separator, a sieve, a specific gravity separator, or the like. This second sorting machine 9 is similar to the first sorting machine 5.
Fine metals and inorganic substances that could not be completely removed are removed and sent to the third pulverizer 11.

第3微粉砕機11に第2選別機9て選別された第2廃棄
物W2と共に適宜な量のクイ・ツクライムを含んだ添加
材が投入される。第3微粉破砕11は例えばリンググラ
イダ−ミルなとを用い、細かな第2廃棄物W2かさらに
微粉末状の第3廃棄物W3になると共に、クイックライ
ムと第3廃棄物W3が均一に混合し接触される。接触さ
れると、′クイックライムであるCaOか第3廃棄物W
3に含まれている水分(H20)とか反応してCa(O
H)2となり、このCa(OH)2か固体である第3廃
棄物W3中に分散される。この反応は第3微粉砕機11
内ではしまり、次の混合貯留反応器13内で完了する。
An additive material containing an appropriate amount of quilling lime is charged into the third pulverizer 11 together with the second waste W2 that has been sorted by the second sorter 9. The third pulverization process 11 is carried out using, for example, a ring glider mill, so that the fine second waste W2 becomes the third waste W3 which is further finely powdered, and the quick lime and the third waste W3 are uniformly mixed. and be contacted. When contacted, 'quick lime CaO or tertiary waste W
Reacts with the water (H20) contained in 3 to form Ca(O
H)2, and this Ca(OH)2 is dispersed in the solid third waste W3. This reaction is carried out in the third pulverizer 11.
It is completed in the next mixing storage reactor 13.

このクイックライムの投入量は廃棄物の投入量に対して
2〜5%好ましくは3%程度を投入する。
The amount of quick lime to be added is about 2 to 5%, preferably about 3%, based on the amount of waste.

第3微粉砕機11て均一に微粉砕化された第3廃棄物W
3と適宜な量のクイックライム(CaOが混合貯溜反応
器13に投入される。混合貯溜反応器13は例えば回転
式6角ミキサ、リボンミキサ、あるいは移動スクリュー
式撹拌機なとからなっていて、貯留されながら一定時間
混合される。
Third waste W uniformly pulverized by the third pulverizer 11
3 and an appropriate amount of quick lime (CaO) are charged into a mixing storage reactor 13.The mixing storage reactor 13 is composed of, for example, a rotary hexagonal mixer, a ribbon mixer, or a moving screw type stirrer. Mixed for a certain period of time while being stored.

この混合貯留反応器13を必要に応じて、熱風や加熱チ
ューブでもって加熱せしめることにより、反応速度を早
くさせることかできる。密閉状態下、例えば温度60℃
以上100℃以下で]時間以上行なうのが好ましい。
The reaction rate can be increased by heating the mixing storage reactor 13 with hot air or a heating tube as necessary. Under closed conditions, e.g. at a temperature of 60°C
It is preferable to carry out the reaction at a temperature of at least 100° C. for a period of at least 100°C.

この混合貯留反応器13で反応して生成された第1生成
廃棄物W4と必要に応じて適宜な量のクイックライムを
含んだ添加材が混合脱気反応器15に投入されて、混合
反応されると共に、アンモニアなどを脱気する。すなわ
ち、排気状態下、前記温度より少なくとも5℃以上高い
温度で5分間以上行なうのが好ましい。次いで、反応さ
れた第2生成廃棄物W、を圧縮成型機17に投入して、
圧縮作用によって密度を高めた上で、押出して粒状に成
型される。この圧縮成型機17て粒状に成型された第3
生成廃棄物W6は乾燥中和反応器19に投入される。こ
の乾燥中和反応器19ては、温度を130〜230℃ま
で上げ、殺菌を行ない、熱化学変化を完了させると共に
、水分を除くと同時に、添加材のアルカリ(CaCoH
):+などをCO2ガスて中和し固化させる。
The first generated waste W4 produced by the reaction in the mixing storage reactor 13 and an additive material containing an appropriate amount of quick lime as needed are put into the mixing deaeration reactor 15, where they are mixed and reacted. At the same time, ammonia etc. are degassed. That is, it is preferable to carry out the heating at a temperature higher than the above temperature by at least 5° C. for 5 minutes or more under exhaust conditions. Next, the reacted second generated waste W is put into the compression molding machine 17,
After increasing the density through compression, it is extruded and formed into granules. The third powder molded into granules by this compression molding machine 17
The produced waste W6 is charged into the drying neutralization reactor 19. In this dry neutralization reactor 19, the temperature is raised to 130 to 230°C, sterilization is carried out, the thermochemical change is completed, water is removed, and the additive alkali (CaCoH) is removed.
): Neutralize and solidify + etc. with CO2 gas.

すなわち、混合貯留反応器13から乾燥中和反応器1つ
までの間で次のような作用が生しる。
That is, the following actions occur between the mixing storage reactor 13 and one dry neutralization reactor.

有機質中に含まれる蛋白質、糖質、脂質は熱とアルカリ
の作用によって変性し、一部は加水分解される。アルカ
リの作用と機械的作用により、紙゛。
Proteins, carbohydrates, and lipids contained in organic matter are denatured by the action of heat and alkali, and some are hydrolyzed. Paper is formed by the action of alkali and mechanical action.

木材、植物残渣なとが、繊維状にはくれると共に細菌は
死滅する。
As the wood and plant residues turn into fibers, the bacteria die.

また、有機質の腐敗又は分解によって生した酸性物質(
H2S、有機酸など)は中和され、アンモニアは揮発す
ると共に、水分か蒸発し、残物は乾燥される。
In addition, acidic substances produced by decay or decomposition of organic matter (
H2S, organic acids, etc.) are neutralized, ammonia is volatilized, water is evaporated, and the residue is dried.

未反応Ca(OH)2はガス中のC02て中和され、不
溶性のCaCO3が生ずると共に、廃棄物中の微粉末は
、添加材中に取り込まれる。
Unreacted Ca(OH)2 is neutralized by CO2 in the gas, producing insoluble CaCO3, and the fine powder in the waste is incorporated into the additive material.

最終的には、添加材は脱水とCaCO3生成て固結し、
他の物質を結びつけ、微粉化された廃棄物は低水分とC
aCO3の被覆により生物学的に安定化される。
Finally, the additive material solidifies through dehydration and CaCO3 production.
Combining other materials, the pulverized waste has low moisture and C
Biologically stabilized by coating with aCO3.

このようにして得られた粒状の廃棄物は、篩分器21で
篩分されて固形物燃料として取出されるのである。
The granular waste thus obtained is sieved by a sieve 21 and taken out as solid fuel.

この篩分器21て篩分された固形物のうち、定の大きさ
より小さな粉体は、一定の大きさに満たされていないた
め、混合貯留反応器13に還流されて再度投入される。
Among the solids sieved by the sieve 21, powders smaller than a certain size are not filled to a certain size, so they are refluxed to the mixing storage reactor 13 and charged again.

前記混合貯留反応器13で貯留されながら混合された第
1生成廃棄物W4は、混合脱気反応器115に投入され
る前に、品質の安定化がチエツクされて、一定の品質に
達成していなければ、混合貯留反応器13に還流される
。この還流される比率は、混合貯留反応器13における
反応時間1反応条件により異なるが、最大50%還流さ
せれば充分であると考える。要は第2生成廃棄物W4の
品質が一定の品質を満足すると、混合脱気反応器15に
投入される。
The first generated waste W4 mixed while being stored in the mixing storage reactor 13 is checked for stabilization of quality and has achieved a certain quality before being input to the mixing degassing reactor 115. If not, it is refluxed to the mixing storage reactor 13. The reflux ratio varies depending on the reaction time and reaction conditions in the mixing storage reactor 13, but it is considered that refluxing at a maximum of 50% is sufficient. In short, when the quality of the second generated waste W4 satisfies a certain quality, it is fed into the mixing degassing reactor 15.

また、混合脱気反応器15で反応された第2生成廃棄物
W5は、圧縮成型機17に投入される前に、一定の反応
達成率か維持されているかどうかのチエツクが行なわれ
て、一定の反応達成率か達成されていなければ、混合貯
留反応器13に還流される。したがって、一定の反応達
成率を維持した第3生成廃棄物W6たけか圧縮成型機1
7に投入されるのである。
In addition, before the second generated waste W5 reacted in the mixed degassing reactor 15 is fed into the compression molding machine 17, a check is performed to see if a constant reaction completion rate is maintained. If the reaction completion rate is not achieved, the mixture is refluxed to the mixing storage reactor 13. Therefore, the third generated waste W6 Takeka compression molding machine 1 that maintained a constant reaction completion rate
It will be put in at 7.

このように、混合貯留反応器13で反応された第1生成
廃棄物W4.混合脱気反応器15て反応された第2生成
廃棄物W5あるいは乾燥中和反応器19で乾燥・中和さ
れて篩分器21で篩分された固形物が、一定の物質的組
成一定の1反応達成率および一定の大きさになるまで何
回でもフィードバックされるようにしであるから、最終
的に得られる固形物(燃料)は均質でクリーンな燃料と
して取出すことができる。
In this way, the first generated waste W4. reacted in the mixing storage reactor 13. The second generated waste W5 reacted in the mixing degassing reactor 15 or the solids dried and neutralized in the drying neutralization reactor 19 and sieved in the sieving device 21 have a constant physical composition. Since the reaction is fed back any number of times until the rate of one reaction is achieved and the size is constant, the solid material (fuel) finally obtained can be taken out as a homogeneous and clean fuel.

第3微粉砕機11から混合脱気反応器15まての工程で
、クイックライムを含んだ添加材を、その各段階で必要
な量だけ投入し、化学反応させて、腐敗性、悪臭を取除
くと共に、生物学的に安定化しであるから、得られた固
形物を燃料として長期貯蔵することができると共に、メ
タンガスが発生してガス爆発などが起きることなく、安
全な燃料として使用することかできる。
In the process from the third pulverizer 11 to the mixing degassing reactor 15, additives containing quick lime are added in the required amount at each stage, and a chemical reaction is caused to remove putrefaction and bad odors. At the same time, it is biologically stabilized, so the obtained solid material can be stored as a fuel for a long period of time, and it can be used as a safe fuel without generating methane gas and causing a gas explosion. can.

なお、この発明は、前述した実施例に限定されることな
く、適宜の変更を行なうことにより、その他の態様で実
施し得るものである。
Note that this invention is not limited to the embodiments described above, and can be implemented in other forms by making appropriate changes.

[発明の効果コ 以上のごとき実施例の説明より理解されるように、この
発明によれば、特許請求の範囲に記載されたとおりの構
成であるから、ごみなどの廃棄物からクリーンな燃料と
なる固形物燃料を得ることができる。また、この得られ
た固形物燃料は、物理的、化学的、生物学的に安定化さ
れているので、長期貯蔵することができる。さらに、ガ
ス爆発や粉じん爆発が発生しない、安全な燃料を提供す
ることができる。
[Effects of the Invention] As can be understood from the explanation of the embodiments described above, according to the present invention, since the structure is as described in the claims, clean fuel can be obtained from waste such as garbage. A solid fuel can be obtained. Furthermore, the obtained solid fuel is physically, chemically, and biologically stabilized, so it can be stored for a long period of time. Furthermore, it is possible to provide a safe fuel that does not cause gas or dust explosions.

しかも、各工程で充分な特性が得られていない場合には
還流させているから、品質の安定した燃料を確保するこ
とかできる。
Moreover, since the fuel is refluxed if sufficient characteristics are not obtained in each step, it is possible to secure fuel of stable quality.

【図面の簡単な説明】[Brief explanation of drawings]

第1図はこの発明を実施する一実施例であり、収集され
た廃棄物から固形物燃料を得る概念的な工程を示す図で
ある。 3・・・第1粗破砕機 5・・・第1選別機7・・・第
2粉砕機 9・・・第2選別機11・・・第3微粉砕機
 13・・・混合貯留反応器15・・・混合脱気反応器
 17・・・圧縮成型・機19・・・乾燥中和反応器 
21・・・篩分器代理人 弁理士 三 好  秀 和
FIG. 1 is an embodiment of the present invention, and is a diagram showing a conceptual process for obtaining solid fuel from collected waste. 3... First coarse crusher 5... First sorter 7... Second crusher 9... Second sorter 11... Third fine crusher 13... Mixing storage reactor 15...Mixing degassing reactor 17...Compression molding/machine 19...Drying neutralization reactor
21... Sieve divider agent Patent attorney Hidekazu Miyoshi

Claims (4)

【特許請求の範囲】[Claims] (1)予め微粉砕された廃棄物と適宜な量のクイックラ
イムを含んだ添加材を混合貯留反応器に投入して混合・
反応を行なった後、反応された第1生成廃棄物を混合脱
気反応器に投入し、適宜な量のクイックライムを含んだ
添加材を必要に応じて添加し、混合反応および反応生成
ガスの脱気を行い、反応された第2生成廃棄物を圧縮成
型機に投入して圧縮成型を行ない、次いで、圧縮成型さ
れた第3生成廃棄物を乾燥中和反応器に投入して乾燥中
和反応を行ない、さらに篩分器にて篩分して固形物燃料
を得ることを特徴とする廃棄物による固形物燃料の製造
方法。
(1) Pre-pulverized waste and additives containing an appropriate amount of quick lime are placed in a mixing storage reactor and mixed.
After carrying out the reaction, the reacted first product waste is put into a mixing degassing reactor, and additives containing an appropriate amount of quick lime are added as necessary to start the mixing reaction and the reaction product gas. Deaeration is performed, and the reacted second product waste is charged into a compression molding machine to perform compression molding, and then the compression molded third product waste is charged into a drying neutralization reactor for drying and neutralization. A method for producing solid fuel from waste, which comprises carrying out a reaction and further sieving in a sieve to obtain solid fuel.
(2)前記混合貯留反応器における反応を密閉状態下、
温度60℃以上100℃以下で1時間以上行い、混合脱
気反応器における反応を排気状態下、前記温度より少く
とも5℃以上高い温度で5分間以上行うことを特徴とす
る請求項(1)記載の廃棄物による固形物燃料の製造方
法。
(2) conducting the reaction in the mixing storage reactor under a closed condition;
Claim (1) characterized in that the reaction is carried out at a temperature of 60° C. or more and 100° C. or less for 1 hour or more, and the reaction in the mixing degassing reactor is carried out under exhaust conditions at a temperature higher than the above temperature by at least 5° C. for 5 minutes or more. A method for producing solid fuel from the described waste.
(3)予め微粉砕された廃棄物とするために、廃棄物を
第1粗破砕機で破砕すると共に不燃物を選別除去し、次
いで第2粉砕機で破砕すると共に廃棄物の複合材中に含
まれている不燃物を選別除去し、さらに、破砕された廃
棄物に適宜な量のクイックライムを含んだ添加材を投入
し、第3微粉砕機で破砕して微粉砕された廃棄物とする
ことを特徴とする請求項(1)記載の廃棄物による固形
物燃料の製造方法。
(3) In order to obtain pre-pulverized waste, the waste is crushed in a first coarse crusher and incombustible materials are sorted and removed, and then crushed in a second crusher and mixed into a waste composite material. Incombustible materials contained in the waste are sorted and removed, and an appropriate amount of additives containing quick lime are added to the crushed waste, which is then crushed in a third pulverizer to form finely pulverized waste. The method for producing solid fuel from waste according to claim (1).
(4)前記反応された第1生成廃棄物、前記脱気反応さ
れた第2生成廃棄物、あるいは前記篩分器にて篩分され
た粉体の廃棄物を必要に応じてかつ、必要な量だけ前記
混合貯留反応器に還流することを特徴とする請求項(1
)記載の廃棄物による固形物燃料の製造方法。
(4) The reacted first product waste, the deaeration-reacted second product waste, or the powder waste sieved by the sieve separator as necessary and as needed. Claim (1) characterized in that the amount of reflux to the mixing storage reactor is
) A method for producing solid fuel from the waste described.
JP2193798A 1990-07-20 1990-07-20 Method of manufacturing solid fuel from waste Expired - Lifetime JP2954990B2 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP2193798A JP2954990B2 (en) 1990-07-20 1990-07-20 Method of manufacturing solid fuel from waste
PCT/JP1991/000961 WO1992001771A1 (en) 1990-07-20 1991-07-19 Method of turning wastes into solid body and method of burning such solid body

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2193798A JP2954990B2 (en) 1990-07-20 1990-07-20 Method of manufacturing solid fuel from waste

Publications (2)

Publication Number Publication Date
JPH0480296A true JPH0480296A (en) 1992-03-13
JP2954990B2 JP2954990B2 (en) 1999-09-27

Family

ID=16313955

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2193798A Expired - Lifetime JP2954990B2 (en) 1990-07-20 1990-07-20 Method of manufacturing solid fuel from waste

Country Status (1)

Country Link
JP (1) JP2954990B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102006013394A1 (en) * 2006-03-23 2007-10-11 Peter Brinkhege Method and device for the treatment of raw wood or the like kiln

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102006013394A1 (en) * 2006-03-23 2007-10-11 Peter Brinkhege Method and device for the treatment of raw wood or the like kiln

Also Published As

Publication number Publication date
JP2954990B2 (en) 1999-09-27

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