JPH01312313A - Garbage incineration equipment - Google Patents

Garbage incineration equipment

Info

Publication number
JPH01312313A
JPH01312313A JP63143802A JP14380288A JPH01312313A JP H01312313 A JPH01312313 A JP H01312313A JP 63143802 A JP63143802 A JP 63143802A JP 14380288 A JP14380288 A JP 14380288A JP H01312313 A JPH01312313 A JP H01312313A
Authority
JP
Japan
Prior art keywords
heat
garbage
concentrator
incinerator
matter
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
Application number
JP63143802A
Other languages
Japanese (ja)
Inventor
Toshimitsu Ichinose
利光 一ノ瀬
Masayasu Sakai
正康 坂井
Kimiyo Tokuda
君代 徳田
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP63143802A priority Critical patent/JPH01312313A/en
Publication of JPH01312313A publication Critical patent/JPH01312313A/en
Pending 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
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To obtain highly economical incineration equipment by comprising a device which uses heat energy for evaporating heat of volatile matter or preheating of incinerator air and garbage. CONSTITUTION:Garbage 1 is cut into small pieces by a cutter 2 inside a hopper 2, then the garbage, which is composed of about 90% of high moisture, is thrown into a vaporizer/concentrator as they are, where the vaporization of moisture and the concentration of solid matter are separated from each other. Since heat must be used to vaporize the volatile matter contained in waste liquid, it is necessary to adopt a differential temperature which is used as a drive source, a heat pump 13 is installed. At the same time, the solid matter or concentrator 21 is thrown into an incinerator 22 which is connected to the vaporization- concentrator 5, and processed through combustion and incineration. Unburnt matter and unburnt gas contained in combustion waste gas 23 discharged from the incinerator 22 are completely removed by a unburnt matter complete incinerator 24. The waste heat is used for preheating the air, while the latent heat of steam after the volatile matter is evaporated is used for evaporating the waste liquid, which makes it possible to perform a perfect processing of waste water in an energy saving manner.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は家庭、都市、工場廃水の処理、生ゴミ処理、汚
水処理、食品廃液処理、し尿処理等に適用されるゴミ焼
却装置に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a garbage incineration device that is applied to household, city, and industrial wastewater treatment, garbage treatment, sewage treatment, food waste liquid treatment, human waste treatment, and the like.

〔従来の技術〕[Conventional technology]

従来廃水処理の主流は生物処理であり、これは貯水槽に
貯留した廃水に空気を送って、有機物をバクテリア分解
させ、ろ過したあと、ろ液は1倍程度の水で希釈したあ
と放水し、残渣物の汚泥は焼却炉で燃料を使って燃焼さ
せていた。
Traditionally, the mainstream of wastewater treatment has been biological treatment, which involves blowing air into wastewater stored in a water tank to decompose organic matter with bacteria, filtering it, and then diluting the filtrate with about 1:1 water before releasing it. The residual sludge was burned using fuel in an incinerator.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

ところで従来方法では、ろ液と残渣物とを別方法で別途
に処理しているため多大の費用と時間を要する不具合が
あった。
However, in the conventional method, the filtrate and the residue are treated separately using different methods, which has the disadvantage of requiring a large amount of cost and time.

本発明は上記不具合を解消した新たな処理装置を提供し
ようとするものである。
The present invention aims to provide a new processing device that eliminates the above-mentioned problems.

〔課題を解決するための手段〕[Means to solve the problem]

このため本発明のゴミ焼却装置は、供給された排水、生
ゴミ等を加熱する蒸発・濃縮器と、上記蒸発・濃縮器に
連結し、該濃縮器で得られる濃縮物を燃焼する燃焼炉と
、上記燃焼炉の出口側から排出される燃焼排ガスと上記
蒸発・濃縮器で得られる揮発物とを加熱浄化する並設セ
ラミックフオームによる加熱・浄化器と、上記加熱・浄
化器からの浄化されたガス及び蒸気の熱エネルギーを上
記揮発物の蒸発用熱又は上記燃焼炉用空気の予熱及び上
記生ゴミの予熱に利用する機構とから構成されることを
特徴としている。
Therefore, the garbage incinerator of the present invention includes an evaporator/concentrator that heats the supplied waste water, garbage, etc., and a combustion furnace that is connected to the evaporator/concentrator and burns the concentrate obtained in the concentrator. , a heating and purifying device using ceramic foam installed in parallel to heat and purify the flue gas discharged from the outlet side of the combustion furnace and volatile matter obtained in the evaporating and concentrating device; It is characterized by comprising a mechanism that utilizes the thermal energy of gas and steam for the heat for evaporating the volatile matter, for preheating the air for the combustion furnace, and for preheating the garbage.

〔作用〕[Effect]

上述の本発明のゴミ焼却装置は、熱を利用して廃水中の
揮発分(一般には全量の70〜90%)を蒸発させ、こ
れには一般にBoD約1%含んでいるのでこれを600
〜1000℃まで加熱することによってBoDと細菌と
を同時に完全焼却し、浄化する。
The waste incinerator of the present invention described above uses heat to evaporate the volatile matter in wastewater (generally 70 to 90% of the total amount), which generally contains about 1% BoD,
BoD and bacteria are completely incinerated and purified at the same time by heating to ~1000°C.

このあと浄化した高温の揮発分蒸気は加熱前の揮発分蒸
気と熱交換させて省エネルギーを図る。このとき揮発分
中の汚れによるスケールの問題を防止する為、別の流体
を熱移送媒体としたヒートパイプ、ヒートポンプを使用
する。
Thereafter, the purified high-temperature volatile vapor is heat-exchanged with the volatile vapor before heating to save energy. At this time, in order to prevent scale problems due to contamination in the volatile matter, a heat pipe or heat pump using another fluid as a heat transfer medium is used.

一方廃水の揮発分蒸発後の残渣汚泥は、燃焼焼却炉で焼
却し、さらに焼却炉で完全燃焼できなかった未燃分、未
燃ガスは焼却炉出口に設けた未燃分焼却装置で完全燃焼
させる。
On the other hand, the residual sludge after the volatile content of wastewater evaporates is incinerated in a combustion incinerator, and the unburned components and gases that could not be completely combusted in the incinerator are completely combusted in an unburned component incinerator installed at the incinerator outlet. let

未燃分完全焼却装置出口の浄化ガス及び蒸気の持つ熱エ
ネルギーは、焼却炉燃焼用空気の予熱に熱交換する。
Thermal energy possessed by the purified gas and steam at the outlet of the complete unburnt incinerator is heat exchanged to preheat the air for combustion in the incinerator.

これにより省エネルギーが可能である。This makes it possible to save energy.

〔実施例〕〔Example〕

以下図面第1図により本発明の一実施例について説明す
ると、第1図は、高水分を含有する廃水酸るいは生ゴミ
処理装置の例を示したものである。
An embodiment of the present invention will be described below with reference to FIG. 1. FIG. 1 shows an example of a wastewater sour or garbage processing apparatus containing high moisture content.

図に於て、生ゴミホッパ2に投入された生ゴミ1は、ホ
ッパ2の内部に装備された切断機3により小片に切断さ
れる。切断された生ゴミ4は約90%の高水分のまま蒸
発・濃縮器5に投入され、ここで水分の蒸発と固形分の
濃縮との分離作用を行なう。蒸発は、後述する廃熱の回
収により行なう為、系外からの熱エネルギーは不要であ
る。
In the figure, food waste 1 put into a food waste hopper 2 is cut into small pieces by a cutting machine 3 installed inside the hopper 2. The cut garbage 4 is fed into the evaporator/concentrator 5 while still having a high moisture content of about 90%, where the separation between evaporation of moisture and concentration of solids is carried out. Evaporation is performed by recovering waste heat, which will be described later, so thermal energy from outside the system is not required.

蒸発した蒸気はミストセパレータ6を通り、連結する過
熱器7で過熱された後加熱室8に投入される。加熱室8
出口排ガスのもつ熱エネルギーは過熱器7の駆動源とな
る。過熱器7で熱を回収された蒸気9は、さらにそれの
もつ熱エネルギーを廃液中揮発分の蒸発用エネルギーと
して回収する。10はヒートパイプで蒸気9のもつ熱エ
ネルギを熱移送媒体としての別流体11に回収し、蒸気
12として熱移送を行なう。この熱を廃液中揮発分の蒸
発に使用する為駆動源となる温度差をとる必要があり、
その為にヒートポンプ13を設置している。これにより
100℃で蒸発する液体14の駆動源として120〜1
40°Cで凝縮する蒸気15をつくることができる。熱
を与えた液体16はヒートパイプ10に循環される。し
たがって、蒸気9の熱は廃液の蒸発熱として利用された
ことになり、清水17として排出される。18は常温マ
で冷却する為のエアフィンである。
The evaporated steam passes through a mist separator 6, is superheated by a connected superheater 7, and then is introduced into a heating chamber 8. Heating chamber 8
The thermal energy of the outlet exhaust gas serves as a driving source for the superheater 7. The steam 9 whose heat has been recovered by the superheater 7 further recovers its thermal energy as energy for evaporating the volatile matter in the waste liquid. A heat pipe 10 recovers the thermal energy of the steam 9 into another fluid 11 as a heat transfer medium, and transfers heat as steam 12. In order to use this heat to evaporate volatile matter in the waste liquid, it is necessary to create a temperature difference that will serve as a driving source.
For this purpose, a heat pump 13 is installed. As a result, 120 to 1
Steam 15 can be produced which condenses at 40°C. The heated liquid 16 is circulated through the heat pipe 10. Therefore, the heat of the steam 9 is used as the heat of evaporation of the waste liquid, and is discharged as fresh water 17. 18 is an air fin for cooling at room temperature.

蒸発・濃縮器5中揮発分の蒸発熱は、さらに別流体19
を媒体に伝えられるヒートパイプ方式としている。加は
伝熱効果を促進する為の回転翼である。
The heat of vaporization of the volatile matter in the evaporator/concentrator 5 is transferred to another fluid 19.
The heat pipe method is used to transmit the heat to the medium. The adder is a rotor blade to promote the heat transfer effect.

一方、固形分または濃縮物21は蒸発・濃縮器5より、
これに連結する焼却炉22に投入され燃焼焼却処理され
る。焼却炉22から排出される燃焼排ガスn中の未燃分
、未燃ガスは未燃分完全焼却装置Uで完全除去され、空
気予熱器部で熱を回収した後煙突26から排出される。
On the other hand, the solid content or concentrate 21 is transferred from the evaporator/concentrator 5.
It is put into the incinerator 22 connected to this and is burned and incinerated. The unburned components and unburned gases in the combustion exhaust gas n discharged from the incinerator 22 are completely removed by the unburned component complete incinerator U, and the heat is recovered by the air preheater section before being discharged from the chimney 26.

加熱室8及び未燃分完全焼却装置24よりなる加熱・浄
化器の出口には、金網又はポーラス状の多孔質のセラミ
ックフオーム27が並設配置され固形分、ばいじん、a
縮物未燃ガス等の完全除去を行ない、輻射エネルギーの
上流側への戻しにより省エネルギーを図っている。28
は加熱・浄化器への燃料供給口であるが、上記輻射エネ
ルギーの有効利用により燃料消費量は少ない。
A wire mesh or a porous ceramic foam 27 is arranged in parallel at the outlet of the heating/purifying device consisting of the heating chamber 8 and the unburnt complete incineration device 24 to remove solids, dust, a
Energy conservation is achieved by completely removing condensates, unburned gas, etc., and returning radiant energy to the upstream side. 28
is the fuel supply port to the heating/purifying device, and the amount of fuel consumed is small due to the effective use of the radiant energy.

固形分又は濃縮物焼却炉22には、空気予熱器5で予熱
された空気29と燃料30が供給される。
The solids or concentrate incinerator 22 is supplied with air 29 preheated by an air preheater 5 and fuel 30.

ただし燃料30は、生ゴミが2000〜3000 TW
/h以上の発熱量を有すれば自燃する為、点火時のみで
良く、自燃しなければ助燃料として供給する。
However, fuel 30 is 2000 to 3000 TW of garbage.
If it has a calorific value of /h or more, it will self-combust, so it only needs to be used at the time of ignition, and if it does not self-combust, it will be supplied as auxiliary fuel.

以上本発明の一実施例について説明したが、本発明はこ
れに限定されることなく、本発明技術思想の範囲内に於
て種々設計変更を施すことができるものである。
Although one embodiment of the present invention has been described above, the present invention is not limited thereto, and various design changes can be made within the scope of the technical idea of the present invention.

〔発明の効果〕〔Effect of the invention〕

本発明のゴミ焼却装置によれば次に示す効果が得られる
According to the garbage incineration device of the present invention, the following effects can be obtained.

(1)  90%以上の水分をもつ各種廃水のうちの大
部分の水分と有機揮発成分を完全浄化し、清水化出来る
(1) It is possible to completely purify most of the water and organic volatile components of various types of wastewater with a water content of 90% or more, resulting in purified water.

(2)残渣汚泥を焼却し、排熱は空気の予熱に、揮発分
蒸発後の蒸気の潜熱は廃液の蒸発に利用することで、経
済性の高い省エネルギー形の廃水完全処理を図ることが
できる。
(2) By incinerating the residual sludge and using the exhaust heat to preheat the air and the latent heat of the steam after volatile matter evaporation to evaporate the waste liquid, complete wastewater treatment can be achieved in a highly economical and energy-saving manner. .

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

第1図は本発明の一実施例装置の全体系統図を示す。 1・・・生ゴミ、5・・・蒸発・濃縮器、6・・・ミス
トセパレータ、7・・・過熱器、8・・・加熱室、10
・・・ヒートパイプ、13・・・ヒートポンプ、20・
・・回転翼、22・・・焼却炉、24・・・未燃分完全
焼却装置、5・・・空気予熱器、26・・・煙突、27
・・・セラミックフオーム。
FIG. 1 shows an overall system diagram of an apparatus according to an embodiment of the present invention. 1... Garbage, 5... Evaporator/concentrator, 6... Mist separator, 7... Superheater, 8... Heating chamber, 10
... heat pipe, 13 ... heat pump, 20.
...Rotary blade, 22...Incinerator, 24...Unburnt complete incineration device, 5...Air preheater, 26...Chimney, 27
...Ceramic form.

Claims (1)

【特許請求の範囲】[Claims] (1)家庭、都市、工場等から排出される排水、生ゴミ
等の処理装置において、供給された上記排水、生ゴミ等
を加熱する蒸発・濃縮器と、上記蒸発・濃縮器に連結し
、該濃縮器で得られる濃縮物を燃焼する燃焼炉と、上記
燃焼炉の出口側から排出される燃焼排ガスと上記蒸発・
濃縮器で得られる揮発物とを加熱浄化する並設した多孔
質のセラミックフォームによる加熱・浄化器と上記加熱
・浄化器からの浄化されたガス及び蒸気の熱エネルギー
を上記揮発物の蒸発用熱又は上記燃焼炉用空気の予熱及
び上記生ゴミの予熱に利用する機構とから構成されるこ
とを特徴とするゴミ焼却装置。
(1) In a treatment device for wastewater, garbage, etc. discharged from homes, cities, factories, etc., an evaporator/concentrator that heats the supplied wastewater, garbage, etc., and a device connected to the evaporator/concentrator, A combustion furnace that burns the concentrate obtained in the concentrator, and a combustion exhaust gas discharged from the outlet side of the combustion furnace and the evaporation and
A heating/purifying device with porous ceramic foam installed in parallel heats and purifies the volatile matter obtained in the concentrator, and the thermal energy of the purified gas and steam from the heating/purifying device is used as heat for evaporating the volatile matter. Or a garbage incinerator characterized by comprising a mechanism utilized for preheating the air for the combustion furnace and preheating the garbage.
JP63143802A 1988-06-13 1988-06-13 Garbage incineration equipment Pending JPH01312313A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63143802A JPH01312313A (en) 1988-06-13 1988-06-13 Garbage incineration equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63143802A JPH01312313A (en) 1988-06-13 1988-06-13 Garbage incineration equipment

Publications (1)

Publication Number Publication Date
JPH01312313A true JPH01312313A (en) 1989-12-18

Family

ID=15347320

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63143802A Pending JPH01312313A (en) 1988-06-13 1988-06-13 Garbage incineration equipment

Country Status (1)

Country Link
JP (1) JPH01312313A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3027191U (en) * 1996-01-25 1996-07-30 神戸農林株式会社 Multipurpose recycling equipment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3027191U (en) * 1996-01-25 1996-07-30 神戸農林株式会社 Multipurpose recycling equipment

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