JP2954990B2 - Method of manufacturing solid fuel from waste - Google Patents
Method of manufacturing solid fuel from wasteInfo
- Publication number
- JP2954990B2 JP2954990B2 JP2193798A JP19379890A JP2954990B2 JP 2954990 B2 JP2954990 B2 JP 2954990B2 JP 2193798 A JP2193798 A JP 2193798A JP 19379890 A JP19379890 A JP 19379890A JP 2954990 B2 JP2954990 B2 JP 2954990B2
- Authority
- JP
- Japan
- Prior art keywords
- waste
- solid fuel
- mixed
- fuel
- reactor
- 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.)
- Expired - Lifetime
Links
- 239000002699 waste material Substances 0.000 title claims description 71
- 239000004449 solid propellant Substances 0.000 title claims description 23
- 238000004519 manufacturing process Methods 0.000 title claims description 11
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 37
- 239000000292 calcium oxide Substances 0.000 claims description 19
- 235000012255 calcium oxide Nutrition 0.000 claims description 19
- 238000006243 chemical reaction Methods 0.000 claims description 16
- 238000003860 storage Methods 0.000 claims description 16
- 239000000654 additive Substances 0.000 claims description 15
- 238000007872 degassing Methods 0.000 claims description 11
- 230000000996 additive effect Effects 0.000 claims description 9
- 238000000748 compression moulding Methods 0.000 claims description 9
- 238000000034 method Methods 0.000 claims description 9
- 238000001035 drying Methods 0.000 claims description 8
- 239000000463 material Substances 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 6
- 238000010438 heat treatment Methods 0.000 claims description 5
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 claims description 4
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 4
- 229910000019 calcium carbonate Inorganic materials 0.000 claims description 2
- 239000001569 carbon dioxide Substances 0.000 claims description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 2
- 239000000446 fuel Substances 0.000 description 18
- 239000007789 gas Substances 0.000 description 14
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 8
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 8
- 239000000126 substance Substances 0.000 description 8
- 239000000203 mixture Substances 0.000 description 7
- 238000007873 sieving Methods 0.000 description 7
- 238000006386 neutralization reaction Methods 0.000 description 6
- 238000004880 explosion Methods 0.000 description 5
- 239000010813 municipal solid waste Substances 0.000 description 5
- 239000007787 solid Substances 0.000 description 5
- 229910021529 ammonia Inorganic materials 0.000 description 4
- 239000011575 calcium Substances 0.000 description 4
- 229910052742 iron Inorganic materials 0.000 description 4
- 239000003513 alkali Substances 0.000 description 3
- 239000000835 fiber Substances 0.000 description 3
- 239000006148 magnetic separator Substances 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 235000019645 odor Nutrition 0.000 description 3
- 239000000123 paper Substances 0.000 description 3
- 238000010992 reflux Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- 238000007664 blowing Methods 0.000 description 2
- 239000011111 cardboard Substances 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 239000010849 combustible waste Substances 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 239000008187 granular material Substances 0.000 description 2
- 230000007774 longterm Effects 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000010850 non-combustible waste Substances 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 229920003023 plastic Polymers 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 101150076749 C10L gene Proteins 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 150000001720 carbohydrates Chemical class 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- -1 earth Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 150000002632 lipids Chemical class 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-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
- 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
Landscapes
- Processing Of Solid Wastes (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
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どから
排出されるごみなど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] [Object of the Invention] (Industrial application field) The present invention treats waste such as garbage discharged from, for example, ordinary households or business establishments, so that it can be reused as fuel. The present invention relates to a method for producing a solid fuel by using waste.
(従来の技術) 従来、例えば一般家庭あるいは事業所などから排出さ
れるごみなどの廃棄物は、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) Conventionally, waste such as refuse discharged from, for example, ordinary households or business establishments has been increasing more and more in recent years, and disposal of this waste has been a problem in any industrialized country. That is the current situation.
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
どに選別されるか、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、環境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
料過程で生ずる有害物質が排ガス処理装置で十分に処理
除去できず大気中に放出する可能性がある。したがっ
て、ごみなど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。Conventionally, this waste is roughly divided into combustible waste and non-combustible waste, and the combustible waste is transported to a waste disposal site for disposal, and the non-combustible waste is crushed and converted into combustible, incombustible, iron, etc. They are either sorted or transported to landfills for landfill disposal. In any case, there is a high risk of environmental pollution. In particular, in the case of incineration, harmful substances often contained in wastes or harmful substances generated in the fuel process of wastes cannot be sufficiently removed by the exhaust gas treatment apparatus and may be released to the atmosphere. Therefore, there are very strict regulations on the incineration of waste such as refuse.
そこで、廃棄物処理業者などでは、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
はなく、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
が行われている。As a result, waste treatment companies have conducted various studies to determine whether they can be reused, rather than simply incinerating them or disposing of them in landfills, as described above. Is being developed for reuse 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%(重量基
準、以下同じ),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,ガラス,
土,石,区分不可能な複合物が5〜15%で、残りが水分
となっていて、低位発熱量として2000〜2500Kcal/kgを
有している。In other words, when examining the composition of waste such as garbage, paper, cardboard, and fibers are 25-45% (by weight, the same applies hereinafter), rubber and plastics are 7-11%, kitchen waste and other combustible materials 7-18%, iron, aluminum, glass,
Soil, stones, and inseparable composites are 5 to 15%, and the remainder is moisture, and has a low calorific value of 2000 to 2500 Kcal / kg.
したがって、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を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 waste is treated and used, a fuel having sufficient energy will be obtained, and development is being attempted by related organizations in various countries to reuse the 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、廃棄物を燃料として再利
用する手段を各機関が試みてきているが、今だ充分に完
成した固形物燃料ができていない。すなわち、ごみなど
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、長期の貯蔵ができないと共
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、圧縮成形する方法も試みられ
ているが、長期間の貯蔵中に吸湿し、同様な問題が生じ
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、燃料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難しかった。(Problems to be Solved by the Invention) By the way, as described above, each institution has been trying to recycle waste as fuel, but a solid fuel which has not been sufficiently completed has been produced. In other words, a method is used in which waste such as garbage is simply crushed to remove incombustibles, but since decay is not completely removed, it is decomposed by microorganisms during storage and cannot be stored for a long time At the same time, a new problem has arisen, such as the emission of odors and flammable gases, causing a gas explosion. To avoid this, crush,
Although a method of further drying and compression molding after sorting is attempted, the same problem occurs due to moisture absorption during long-term storage. Further, a method has been attempted in which solid briquettes are formed by melting plastic contained in wastes, for example, but only solid fuels having poor fuel properties have been obtained. Furthermore, since refuse basically contains combustible nitrogen, volatile chlorine, sulfur, etc., it has been difficult to produce clean fuel from refuse until now.
この発明の目的は、上記問題点を改善し、腐敗性を取
除き、長期貯蔵ができ、しかも悪臭やガス爆発を起さな
いようにすると共に、燃料性がよく、クリーンな燃料を
得るようにした廃棄物による固形燃料の製造方法を提供
することにある。An object of the present invention is to improve the above-mentioned problems, remove spoilage, allow long-term storage, prevent odors and gas explosions, and provide a clean fuel with good fuel properties. It is an object of the present invention to provide a method for producing a solid fuel by using 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、60℃以上10
0℃以下の温度で加熱した混合貯留反応器に、予め破砕
された廃棄物とクイックライムを含んだ添加剤を投入し
て混合加熱反応させ、脱気後、圧縮成形し、さらに乾燥
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 relates to
Into a mixing and storage reactor heated at a temperature of 0 ° C. or less, an additive containing pre-crushed waste and quick lime is added and mixed and heated and reacted.After degassing, compression molding, and further drying and solidification are performed. This is a method for producing solid fuel from waste to obtain solid fuel.
また、前記製造方法において、クイックライムを廃棄
物に対して2〜5重量%、好ましくは3重量%混合する
ことが望ましい。In the above-mentioned manufacturing method, it is desirable to mix 2-5% by weight, preferably 3% by weight of quick lime with respect to the waste.
脱気を加熱して行うこと、さらにこれを熱風の吹き込
みによってなすことが望ましいものである。It is desirable that the degassing be performed by heating, and that this be performed by blowing hot air.
また、乾燥は炭酸ガスを含むガス中で、130℃以上230
℃以下で行ない、炭酸カルシウムを生成させること、お
よび乾燥後篩分を行い一定寸法以下の固形物燃料を混合
反応工程に還流させ高品質の固形物燃料を得ることが、
望ましい。Drying is performed in a gas containing carbon dioxide gas at 130 ° C or more and 230 ° C.
° C. or less, to produce calcium carbonate, and sieving after drying, to reflux solid fuel of a certain size or less to the mixing reaction step to obtain a high quality solid fuel,
desirable.
(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、予め破砕された廃棄物は、ごみなどの
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例えば上述の
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
添加剤を投入し、第3細破砕機で破砕することによっ
て、破砕された廃棄物と添加剤が混ぜられたものとして
得られる。(Operation) By employing the method for producing a solid fuel from waste according to the present invention, the previously crushed waste is obtained by crushing waste such as refuse by a first coarse crusher and selectively removing incombustibles. And then crushed by a second crusher and, for example, selectively removing incombustible substances contained in the above-described composite material,
By adding an appropriate amount of an additive containing quick lime to the crushed waste and crushing it with a third crusher, the crushed waste and the additive are obtained as a mixture.
こうして得られた破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剤の混合物を60℃以上100℃以
下の温度で加熱した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(CaO)が
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、反応が進み、貯留しながら混合して品質が均
一化した破砕された第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剤を添加す
ると同様な反応によって温度が上昇し、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、この工程は添加剤を添加せず、混合脱気反応器中
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形
機に投入し、粒状に成形された第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。The mixture of the crushed waste obtained in this manner and an additive containing an appropriate amount of quick lime is charged into a mixed storage reactor heated at a temperature of 60 ° C or higher and 100 ° C or lower, whereby the water content of the waste is reduced. And quick lime (CaO) react with each other to form Ca (OH) 2 , and the reaction proceeds while the temperature rises due to the heat of reaction. can get. The obtained first product waste is charged into a mixed degassing reactor, and further, an appropriate amount of an additive containing quick lime is added to increase the temperature by the same reaction, and a reaction containing steam and ammonia is performed. Since gas is generated, this is eliminated.
In this step, it is also possible to generate a reactive gas by blowing hot air into the mixed degassing reactor or heating the waste by another appropriate method without adding an additive. The second product waste thus obtained is put into a compression molding machine to obtain a third product waste formed into a granular form.
Next, the third product waste is put into a dry neutralization reactor to be dried, and further sieved with a sieving device to obtain a 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が得られる。In the step, the second product waste, the third product waste, or the sieved powder is refluxed to the mixed storage reactor as necessary and in a necessary amount, so that an efficient solid material is obtained. Fuel is 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。Hereinafter, embodiments of the present invention will be described in detail with reference to 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
から排出されるごみなどの廃棄物Wは、紙,段ボール,
繊維類などの可燃物と、鉄,アルミ,ガラス,土,石な
どの不燃物と、これらに含まれる水分などで構成されて
おり、トラック,パッカー車などの運搬車などで運ばれ
てきて、一旦ホッパー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。Referring to FIG. 1, for example, waste W such as garbage discharged from a general household or business is made of paper, cardboard,
It is composed of combustible materials such as fibers, incombustible materials such as iron, aluminum, glass, earth, and stone, and moisture contained in these materials, and is transported by trucks, packers, and other transport vehicles. Once put into the hopper 1. This hopper 1
The required amount is supplied to 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
省略するが、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 crushing machine 3 is, for example, a hydraulic low-speed driven tearing coarse crushing machine, and has a specific structure known in the art. 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、回転数がそれぞれ異な
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,低トルクに
て、負荷増大時に低速,高トルク運転と負荷に応じて軸
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。Thus, the input waste is gripped by a two- or three-axis rotary tearing blade having different rotation speeds, and tearing is performed.
It breaks through to a strong object, is slowly torn by low-speed, high-torque hydraulic drive, and is discharged from the discharge port at the bottom of the main body. The first coarse crusher 3 is driven by a hydraulic drive system. By using a variable discharge axial piston pump, the first coarse crusher 3 is driven at high speed and low torque at normal load, and at low speed and high torque at load increase. Since the shaft rotation speed can be varied according to the operation and the load, the operation control can always be performed in an optimal state with respect to the crushing load.
この第1粗破砕機3で粗破砕された第1廃棄物W1は、
例えばベルトコンベアなどからなる第1選別機5に送ら
れる。この第1選別機5には磁選機が備えられていて、
その磁選機により鉄などの金属が除去される。また、第
1選別機では、ビン,ブロックなどの中形無機物が選別
されて除去される。The first waste W 1 coarsely crushed by the first coarse crusher 3 is
For example, it is sent to a first sorter 5 composed of a belt conveyor or the like. This first sorter 5 is provided with a magnetic separator,
The magnetic separator removes metals such as iron. In the first sorting machine, medium-sized inorganic substances such as bottles and blocks are sorted 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破砕機7に送られる。第2破砕機7は例え
ばハンマミルなどからなっており、この第2破砕機7で
廃棄物W1はさらに細かく破砕される。Metal in the first sorter 5, the inorganic substance is removed, the first waste W 1 is sent to the second crusher 7. Second crusher 7 is made of, for example, hammer mill, waste W 1 in the second crusher 7 is further finely crushed.
第2破砕機7で細かく破砕された第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では、第1選別機
5で除去しきれなかった細かな金属や無機物が除去され
て、第3細破砕機11に送られる。Second waste W 2 is which is finely crushed in a second crusher 7, sent for example magnetic separator, sieving device, to the second sorter 9 made of difference in specific gravity separator. In the second sorter 9, fine metals and inorganic substances that cannot be completely removed by the first sorter 5 are removed and sent to the third shredder 11.
第3細破砕機11に第2選別機9で選別された第2廃棄
物W2と共に適宜な量のクイックライムを含んだ添加剤が
投入される。第3細破砕機11は、例えばリンググライダ
ーミルなどを用い、細かな第2廃棄物W2がさらに細破砕
物状の第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。接触すると、クイ
ックライムのCaOが第3廃棄物W3に含まれている水分(H
2O)と反応してCa(OH)2となり、このCa(OH)2が固
体である第3廃棄物W3中に分散される。この反応は第3
細破砕機11内ではじまり、次の混合貯留反応器13内で完
了する。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。Second waste W additives containing appropriate quantities of quick lime with 2 sorted by the second sorter 9 is turned to the third fine crusher 11. Third fine crusher 11, for example ring glider mill using a quick lime and a third with fine second waste W 2 is in the third waste W 3 further fine crushed like
Waste W 3 are uniformly mixed in contact. Upon contact, the moisture CaO quick lime is included in the third waste W 3 (H
2 O) reacts with Ca (OH) 2, and this Ca (OH) 2 is dispersed to the third in the waste W 3 is solid. This reaction is the third
It starts in the crusher 11 and is completed in the next mixed storage reactor 13. The amount of the quick lime is 2 to 5%, preferably about 3%, based on the amount of the waste.
第3細破砕機11で均一に破砕された第3廃棄物W3と適
宜な量のクイックライムが混合貯留反応器13に投入され
る。混合貯留反応器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どから
なっていて、貯留されながら一定時間混合される。この
混合貯留反応器13を熱風や加熱チューブでもって加熱せ
しめることにより、反応速度を速くさせることができ
る。密閉状態下、温度60℃以上100℃以下で反応時間は1
5分程度で可能であるが、1時間以上行なうのが好まし
い。Appropriate amount of quick lime is added to a mixed reservoir reactor 13 and the third waste W 3 that is uniformly crushed in third fine crusher 11. The mixing and storing reactor 13 is composed of, for example, a rotary hexagonal mixer, a ribbon mixer, or a moving screw type stirrer, and is mixed for a predetermined time while being stored. By heating the mixed storage reactor 13 with hot air or a heated tube, the reaction speed can be increased. The reaction time is 1 at a temperature of 60 ° C or higher and 100 ° C or lower in a closed state.
Although it is possible in about 5 minutes, it is preferable to carry out for 1 hour or more.
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
んだ添加剤が混合脱気反応器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、
廃棄状態下、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W5を圧縮成形機17に投入して、圧縮作用
によって密度を高めた上で、押出して粒状に成形され
る。この圧縮成形機17で粒状に成形された第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では、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、添加剤由来のアルカリ(Ca(OH)2)などをCO2ガ
スで中和し固化させる。The mixture reservoir reactor 13 additives containing appropriate quantities of quick lime optionally a first product waste W 4 which is produced by the reaction in is added to a mixed degassing reactor 15, mixed reaction At the same time, degas ammonia and the like. That is,
It is preferable to carry out at a temperature at least 5 ° C. higher than the above-mentioned temperature for 5 minutes or more in a waste state. Then put the second product waste W 5 which is reacted in the compression molding machine 17, after densified by compression action is shaped extruded into granules. The third product waste W 6 formed into granules by the compression molding machine 17 is charged into a dry neutralization reactor 19. In the drying and neutralization reactor 19, the temperature is increased to 130 to 230 ° C., sterilization is performed, thermochemical changes are completed, moisture is removed, and at the same time, alkali (Ca (OH) 2 ) derived from additives is removed. Neutralize and solidify with CO 2 gas.
すなわち、混合貯留反応器13から乾燥中和反応器19ま
での間で次のような作用が生じる。That is, the following operation occurs between the mixed storage reactor 13 and the dry neutralization reactor 19.
有機質中に含まれる蛋白質,糖質,脂質は熱と添加剤
に含まれる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,
木材,植物残渣などが、繊維状にほぐれると共に細菌は
死滅する。Proteins, carbohydrates and lipids contained in organic matter are denatured and partially hydrolyzed by the action of heat and alkali contained in additives. By the action of alkali and mechanical action, paper,
Bacteria are killed as wood and plant residues are unraveled into fibers.
また、有機質の腐敗又は分解によって生じた酸性物質
(H2S,有機酸など)は中和され、アンモニアは揮発する
と共に、水分が蒸発し、廃棄物は乾燥される。In addition, acidic substances (H 2 S, organic acids, etc.) generated by organic decay or decomposition are neutralized, ammonia evaporates, moisture evaporates, and waste is dried.
クイックラムから生成されたCa(OH)2は、乾燥ガス
中のCO2で中和され、不溶性のCaCO3が生ずると共に、廃
棄物は、これに被覆される。Quick Ca (OH) 2 produced from the ram is neutralized with CO 2 in the drying gas, with CaCO 3 occurs insoluble, waste is coated thereto.
最終的には、添加剤は脱水とCaCO3生成で固結し、他
の物質を結びつけ、破砕された廃棄物は、低水分とCaCO
3の被覆により生物学的に安定化される。Ultimately, the additives solidify by dehydration and CaCO 3 generation, linking other substances, and the crushed wastes have low moisture and CaCO 3
Biologically stabilized by the coating of 3 .
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 the sieving device 21 and is taken out as solid fuel.
この篩分器21で篩分された固形物のうち、一定の大き
さより小さい固形物は、一定の大きさを満たすために、
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 sieving device 21, solids smaller than a certain size are required to satisfy a certain size.
The mixed storage reactor 13 is refluxed 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15に投入される前
に、品質の安定化がチェックされて、例えばpH値の変動
など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、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。要は、第1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。First generating waste W 4 which are mixed while being stored in the mixing reservoir reactor 13, before being added to a mixed degassing reactor 15, is checked stable quality, for example, variations in pH value, etc. If a certain quality is not achieved, a mixed storage reactor
Refluxed to 13. This reflux ratio varies depending on the reaction time and reaction conditions in the mixed storage reactor 13, but the maximum
50% reflux is sufficient. In short, first generation waste W 4
When the quality of the mixture satisfies a certain level, the mixture is charged into the mixed deaeration 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、圧縮成形器17に投入される前に、pH値および排ガ
ス中のアンモニア濃度を測定し一定の反応達成率が維持
されているかどうかのチェックが行なわれて、一定の反
応達成率が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2生成廃棄物W5だけが圧縮成形機17に投入されるので
ある。Also, the second product waste reacted in the mixed degassing reactor 15
W 5, before being introduced into the compression molding apparatus 17, pH value and whether the check is performed ammonia concentration measured constant reaction achievement ratio in the exhaust gas is maintained, certain reaction achievement rate If not achieved, it is refluxed to the mixed storage reactor 13. Therefore, only the second product waste W 5 maintaining a constant reaction achievement rate is being introduced in the compression molding machine 17.
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で反応された第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
反応達成率および一定の大きさになるまで何回でも還流
されるようにしてあるから、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。As described above, the first product waste W 4 reacted in the mixed storage reactor 13, the second product waste W 5 reacted in the mixed degassing reactor 15, or dried and neutralized in the dry neutralization reactor 19. The solids that have been sieved and sieved by the sieving device 21 are repeatedly refluxed until they reach a certain material composition, a certain reaction achievement rate, and a certain size. The resulting solid fuel can be removed as a homogeneous and clean fuel.
第3細破砕機11から混合脱気反応器15までの工程で、
クイックライムを含んだ添加剤を、その各工程で必要な
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てあるから、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ができる。In the process from the third crusher 11 to the mixed degassing reactor 15,
Additives containing quick lime are added in the required amount in each step and chemically reacted to remove spoilage and bad odor. It can be stored as fuel for a long time, and can be used as a safe fuel without generating methane gas and causing gas explosion.
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。The present invention is not limited to the above-described embodiment, but can be embodied in other modes by making appropriate changes.
[発明の効果] 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、クイックライムを含む添加剤と廃棄
物が加熱反応処理され、その反応達成率が確実で高く、
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 description of the embodiments as described above, according to the present invention, since the configuration is as described in the claims, clean fuel from waste such as garbage can be obtained. Solid fuel can be obtained. In addition, the obtained solid fuel is subjected to a heat reaction treatment of an additive containing quick lime and waste, and the reaction achievement rate is reliable and high,
It is physically, chemically and biologically stabilized and can be stored for long periods. Further, it is possible to provide a safe fuel that does not cause a gas explosion or a dust explosion.
しかも、必要に応じ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るこ ともでき、品質の安定した燃料を確保することができ
る。In addition, if sufficient characteristics are not obtained in each step, the fuel can be refluxed if necessary, and a fuel of stable quality can be secured.
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。 1……ホッパー、3……第1粗破砕機、5……第1選別
機、7……第2破砕機 9……第2選別機、11……第3細破砕機、13……混合貯
留反応器 15……混合脱気反応器、17……圧縮成形機、19……乾燥
中和反応器 21……篩分器、CaO……クイックラムを含む添加剤FIG. 1 is an embodiment of the present invention, showing a conceptual process for obtaining solid fuel from collected waste. DESCRIPTION OF SYMBOLS 1 ... Hopper, 3 ... 1st coarse crusher, 5 ... 1st sorter, 7 ... 2nd crusher 9 ... 2nd sorter, 11 ... 3rd fine crusher, 13 ... Mixing Storage reactor 15: Mixed degassing reactor, 17: Compression molding machine, 19: Dry neutralization reactor 21: Sieving device, CaO: Additive including quick ram
フロントページの続き (58)調査した分野(Int.Cl.6,DB名) C10L 5/46 - 5/48 B09B 3/00 WPI/L(QUESTEL)Continuation of the front page (58) Field surveyed (Int. Cl. 6 , DB name) C10L 5/46-5/48 B09B 3/00 WPI / L (QUESTEL)
Claims (6)
貯留反応器に、予め破砕された廃棄物とクイックライム
を含んだ添加剤を投入して混合加熱反応させ、脱気後、
圧縮成形し、さらに乾燥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. A mixed storage reactor heated at a temperature of 60 ° C. or more and 100 ° C. or less is charged with an additive containing preliminarily crushed waste and quick lime, and mixed and heated to react.
A method for producing solid fuel from waste, comprising compression molding and drying to obtain a solid fuel.
量%混合することを特徴とする請求項(1)に記載の廃
棄物による固形物燃料の製造方法。2. The method for producing solid fuel from waste according to claim 1, wherein 2-5% by weight of the quick lime is mixed with the waste.
項(1)〜(2)のいずれかに記載の廃棄物による固形
物燃料の製造方法。3. The method according to claim 1, wherein the degassing is performed by heating.
る請求項(1)〜(3)のいずれかに記載の廃棄物によ
る固形物燃料の製造方法。4. The method for producing a solid fuel from waste according to claim 1, wherein hot air is blown out of the air.
上230℃以下で行い、炭酸カルシウムを生成させること
を特徴とする請求項(1)〜(4)のいずれかに記載の
廃棄物による固形物燃料の製造方法。5. The disposal according to claim 1, wherein the drying is performed in a gas containing carbon dioxide at a temperature of 130 ° C. or more and 230 ° C. or less to generate calcium carbonate. A method for producing a solid fuel by using a material.
工程に還流させることを特徴とする請求項(1)〜
(5)のいずれかに記載の廃棄物による固形物燃料の製
造方法。6. The method according to claim 1, wherein the solid fuel having a certain size or less is refluxed in the mixing and heating reaction step.
(5) The method for producing a solid fuel from waste according to any of (5).
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 JPH0480296A (en) | 1992-03-13 |
JP2954990B2 true 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) |
Families Citing this family (1)
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 |
-
1990
- 1990-07-20 JP JP2193798A patent/JP2954990B2/en not_active Expired - Lifetime
Also Published As
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JPH0480296A (en) | 1992-03-13 |
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