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JPH062274B2 - Waste treatment equipment using ships - Google Patents
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JPH062274B2 - Waste treatment equipment using ships - Google Patents

Waste treatment equipment using ships

Info

Publication number
JPH062274B2
JPH062274B2 JP1286889A JP28688989A JPH062274B2 JP H062274 B2 JPH062274 B2 JP H062274B2 JP 1286889 A JP1286889 A JP 1286889A JP 28688989 A JP28688989 A JP 28688989A JP H062274 B2 JPH062274 B2 JP H062274B2
Authority
JP
Japan
Prior art keywords
waste
wastes
irradiation
wood
far
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
Application number
JP1286889A
Other languages
Japanese (ja)
Other versions
JPH03151089A (en
Inventor
勝昭 高橋
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP1286889A priority Critical patent/JPH062274B2/en
Publication of JPH03151089A publication Critical patent/JPH03151089A/en
Publication of JPH062274B2 publication Critical patent/JPH062274B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B63SHIPS OR OTHER WATERBORNE VESSELS; RELATED EQUIPMENT
    • B63BSHIPS OR OTHER WATERBORNE VESSELS; EQUIPMENT FOR SHIPPING 
    • B63B35/00Vessels or similar floating structures specially adapted for specific purposes and not otherwise provided for
    • B63B35/44Floating buildings, stores, drilling platforms, or workshops, e.g. carrying water-oil separating devices
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B63SHIPS OR OTHER WATERBORNE VESSELS; RELATED EQUIPMENT
    • B63BSHIPS OR OTHER WATERBORNE VESSELS; EQUIPMENT FOR SHIPPING 
    • B63B35/00Vessels or similar floating structures specially adapted for specific purposes and not otherwise provided for
    • B63B35/44Floating buildings, stores, drilling platforms, or workshops, e.g. carrying water-oil separating devices
    • B63B2035/4426Stationary floating buildings for human use, e.g. floating dwellings or floating restaurants
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/30Pyrolysing
    • F23G2201/302Treating pyrosolids
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2206/00Waste heat recuperation
    • F23G2206/10Waste heat recuperation reintroducing the heat in the same process, e.g. for predrying
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A30/00Adapting or protecting infrastructure or their operation

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • Architecture (AREA)
  • Civil Engineering (AREA)
  • Structural Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Combustion & Propulsion (AREA)
  • Ocean & Marine Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、都市ゴミ及び各種の産業廃棄物を船舶を利用
して洋上処理する装置に関するもので、更に詳細には、
施設用地確保の問題がなく、且つ、遠赤外線の照射処理
によって比較的低温で有効成分の再生利用が可能な手段
に関するものである。
Description: TECHNICAL FIELD The present invention relates to an apparatus for treating municipal refuse and various industrial wastes offshore using a ship, and more specifically,
The present invention relates to a means for reusing an active ingredient at a relatively low temperature by irradiation treatment with far infrared rays without the problem of securing a site for a facility.

(従来の技術) 現在都市ゴミ及び各種の産業廃棄物については、各自治
体が焼却設備を設け、回収したゴミを焼却炉にて処分
し、その灰を埋立地に埋めているが、増大する一方の廃
棄物に対し埋立地等の増設がこれに追いつかないのが現
状である。特に都市部では、地下の高騰と地域住民の反
対等により処理能力極端に不足し、生活環境に支障がで
ることが憂慮されている。
(Prior Art) Currently, regarding municipal waste and various industrial wastes, each municipality has installed an incineration facility, disposes of the collected waste in an incinerator, and burys the ash in a landfill, but this is increasing. The current situation is that the expansion of landfills, etc., cannot keep up with the waste of the above. Especially in urban areas, it is feared that the processing capacity will be extremely insufficient due to soaring underground and the opposition of local residents, which will hinder the living environment.

これに対し、従来解決の一手段として港湾等で処理する
技術が特開昭63−31901号、63−255194
号公報等に提案されている。
On the other hand, as a conventional solution, a technique of processing at a port or the like is disclosed in JP-A-63-31901 and 63-255194.
It has been proposed in the Japanese publication.

しかし、この処理を技術的に見ると、廃棄物を全て燃焼
させてしまう焼却という方法が採られているため、下記
の問題を残すことになる。
However, from a technical point of view of this treatment, since the method of incineration that burns all the waste is adopted, the following problems remain.

即ち、この方法は、a)高温下で処理するため設備の損
傷が激しく、補修費用等の運転経費が甚大で経済的負担
が重く、b)廃棄物のなかには再利用可能な有効成分が
多分に存し、これを燃焼という形で捨て去ってしまうの
は資源利用の点から好ましくなく、c)更に、燃焼の際
発生する塩素ガスや二酸化炭素等の廃棄ガスは、人体に
有害であるばかりか、地球温暖化の一要因となるもので
環境汚染の原因となる面からも問題を残している。
That is, in this method, a) the treatment is performed at a high temperature, the equipment is severely damaged, the operating cost such as repair cost is great and the economical burden is heavy, and b) the reusable active ingredient is probably contained in the waste. However, it is not preferable from the viewpoint of resource utilization to dispose of it in the form of combustion. C) Furthermore, waste gases such as chlorine gas and carbon dioxide generated during combustion are not only harmful to the human body, It is a factor that contributes to global warming and remains a problem in terms of causing environmental pollution.

(発明の解決しようとする課題) 本発明は上記実情に鑑みてなされたもので、土地問題の
比較的少ない洋上に目を向け、且つ、燃焼という手段を
離れて、遠赤外線を利用した低温照射処理により有効成
分の回収と環境保全の図れる手段を開発したものであ
る。
(Problems to be Solved by the Invention) The present invention has been made in view of the above-mentioned circumstances, and the low temperature irradiation using far infrared rays is aimed at the ocean where the land problem is relatively small, and away from the means of combustion. This means that we have developed means to recover the active ingredient and to protect the environment through treatment.

(課題を解決するための手段) 本発明廃棄物処理装置は、船舶内に、生ゴミ等の都市ゴ
ミ及び漁業廃棄物、水産加工物、食品加工物、木材加工
廃棄物、木材建材廃棄物等の産業廃棄物の収納ケースを
搭載する手段を有する。そして、その廃棄物の周囲を遠
赤外線放射セラミックスで無酸素状態に密閉し、且つ、
その処理物に適した温度下で遠赤外線放射を照射加熱し
て気化及び/又は炭化する加熱手段を付与すると共に、
その熱排気が前記セラミックスの外側を囲尭する二重層
に形成した照射炉を有する。そして、該照射処理によっ
て得られた木酢、カーボン等の有効成分を保管する格納
手段とを船舶内に備えたことを特徴として構成される。
(Means for Solving the Problem) The waste treatment device of the present invention is provided on a ship with municipal waste such as raw garbage and fishery waste, marine product processed food, processed food, wood processing waste, wood building material waste, etc. It has a means for mounting the industrial waste storage case. Then, the periphery of the waste is hermetically sealed with far-infrared radiation ceramics, and
A heating means for irradiating and heating far infrared radiation at a temperature suitable for the processed material to vaporize and / or carbonize is provided, and
It has an irradiation furnace whose thermal exhaust is formed in a double layer surrounding the outside of the ceramics. The vessel is equipped with a storage means for storing active ingredients such as wood vinegar and carbon obtained by the irradiation treatment.

(作用) 都市ゴミ及び各種の産業廃棄物を無酸素状態に密閉し、
且つ、処理目的に適した温度下で遠赤外線を照射する
と、先ず内部の液状物が赤外活性により吸収共鳴し、木
酢等の液状物が気化され、更に若干温度を上昇させて照
射を続けると、有機質が炭化され、低温で処理ができ
る。この際、焼却処理ではないので、燃焼ガスが出ない
ので、二次的環境汚染の問題がでない。
(Action) Municipal waste and various industrial waste are hermetically sealed,
And, when irradiated with far infrared rays at a temperature suitable for the purpose of treatment, first the liquid substance inside absorbs resonance due to infrared activity, the liquid substance such as wood vinegar is vaporized, and the temperature is further raised to continue irradiation. , The organic matter is carbonized and can be processed at low temperature. At this time, since it is not an incineration process, no combustion gas is emitted, so there is no problem of secondary environmental pollution.

この照射処理を、船舶を利用して洋上で行なうので、土
地問題が解消される。
Since this irradiation processing is performed on the ocean using a ship, the land problem is solved.

寄港後にその処理で得た木酢、カーボン等の有効成分を
回収することができるので無駄がない。
After arriving at the port, the active ingredients such as wood vinegar and carbon obtained by the treatment can be recovered, so there is no waste.

(装置の実施例) 本発明装置の実施例を示した第1図において、1が船舶
で、その先端には港湾に積載したコンテナ等の収納ケー
ス2を搭載するクレーン3等の積載手段を有する。該収
納ケース2には、生ゴミ等の都市ゴミ、及び漁業廃棄
物、水産加工物、食品加工廃棄物、木造建材廃棄物等の
産業廃棄物を二次生産品別に分類して収納しておく。4
がそのコンテナを移送させるコンベヤ等の搬送手段であ
る。5が船室内又は甲板上に設ける遠赤外線の照射炉
で、6が処理後の有効成分を保管する格納庫である。
(Embodiment of Device) In FIG. 1 showing an embodiment of the device of the present invention, reference numeral 1 is a ship, and a tip end thereof has a loading means such as a crane 3 for loading a storage case 2 such as a container loaded in a harbor. . The storage case 2 stores therein city garbage such as raw garbage, and industrial waste such as fishery waste, marine product, food processing waste, and wooden construction material waste classified by secondary products. . Four
Is a conveying means such as a conveyor for transferring the container. Reference numeral 5 is a far-infrared irradiation furnace provided in the cabin or on the deck, and 6 is a hangar for storing the treated active ingredients.

そして、照射炉5の詳細は第2図に示す如くで、中央に
無酸素状態に遮蔽可能な照射室10を設け、その上部に
廃棄物の投入口11を配し、下部に炭化後のカーボン等
を取り出す取出口12を配し、周囲を遠赤外線照射セラ
ミックス13で囲繞する。この遠赤外線照射セラミック
ス13は、例えば焼成白磁10%、アルミナ53%、酸
化第一鉄5%、炭素10%、シリカ5%の粉末を混合
し、アルミナセメント5%、水12%を加えて混練して
成型したもので構成し、これは7〜14μの領域で強い
放射特性を有する。
The details of the irradiation furnace 5 are as shown in FIG. 2. An irradiation chamber 10 that can be shielded in an oxygen-free state is provided at the center, a waste input port 11 is provided at the upper part thereof, and carbonized carbon is provided at the lower part. An outlet 12 for taking out the above is arranged, and the periphery is surrounded by far-infrared irradiation ceramics 13. This far-infrared irradiation ceramics 13 is, for example, mixed with powders of 10% calcined white porcelain, 53% alumina, 5% ferrous oxide, 10% carbon, and 5% silica, and kneaded by adding 5% alumina cement and 12% water. And has a strong radiation characteristic in the region of 7 to 14 μm.

その照射室10の周囲を下部に加熱バーナー15を臨ま
せた加熱室14で覆い、側壁部に加熱空気が遠赤外線照
射セラミックス13に接触して上昇するよう区画壁16
で螺旋状に巻設し、上部に煙筒17を立設する。
The periphery of the irradiation chamber 10 is covered with a heating chamber 14 having a heating burner 15 facing the lower part thereof, and a partition wall 16 is provided on the side wall so that the heated air comes in contact with the far infrared irradiation ceramics 13 and rises.
Is wound in a spiral shape, and the smoke pipe 17 is erected on the upper part.

又、照射室10の上部一方には、照射処理によって発生
するガス体を排出する排気口18を設け、これに排気管
19を連結するが、その途中に切換弁20を介して再流
管21を接続し、最初発生した蒸気を排出させた後、炭
化工程に移ったら切換弁20を作動させて再流管21に
より加熱バーナー15に戻し、燃焼ガスとして利用でき
るようにする。
Further, an exhaust port 18 for exhausting a gas body generated by the irradiation process is provided on one upper side of the irradiation chamber 10, and an exhaust pipe 19 is connected to the exhaust port 18, and a reflow pipe 21 via a switching valve 20 in the middle thereof. After discharging the generated steam, the switching valve 20 is operated and returned to the heating burner 15 by the reflow pipe 21 when the carbonization process is started, so that it can be used as combustion gas.

そして、この照射炉5は、廃棄物が一種類の場合は、大
型の炉を一基設置すれば良いが、多種類に渡る場合には
複数個設ける。
If the waste is of one type, one large furnace may be installed, but if there are many types of waste, a plurality of irradiation furnaces 5 may be provided.

この結果、本発明装置は、廃棄物を無酸素状態で照射加
熱して気化及び又は炭化する照射処理するので、炭酸ガ
ス等の排気ガスを多量に発生することがなく、公害問題
を生じない処理が可能となる。
As a result, the apparatus of the present invention performs irradiation treatment in which waste is irradiated and heated in an oxygen-free state to be vaporized and / or carbonized, so that a large amount of exhaust gas such as carbon dioxide gas is not generated and a pollution problem does not occur. Is possible.

又、遠赤外線を廃棄物の性質に合せて利用するので、本
来高温を要求される分解ガス化を比較的低温で行うこと
ができ、狭い船舶内にあっても、装置の大型化を避け
て、コンパクトにまとめることが可能となる。
In addition, since far infrared rays are used according to the nature of the waste, it is possible to perform decomposition gasification, which originally requires high temperatures, at relatively low temperatures, and avoid increasing the size of the equipment even in a narrow ship. , It becomes possible to put it together compactly.

更に、放射セラミックスの外側を照射炉の熱排気で二重
層に覆うので、その排気熱を利用してセラミックスが効
率良く遠赤外線を放射することができ、電源や熱源の供
給が極めて制限される船舶で、新たな熱源を要しない点
で優れている。
Further, since the outside of the radiant ceramics is covered with the thermal exhaust of the irradiation furnace in a double layer, the ceramics can efficiently radiate far infrared rays by utilizing the exhaust heat, and the supply of power source and heat source is extremely limited. It is excellent in that it does not require a new heat source.

(試験例1) 〈建築廃材、木材廃材の場合〉 廃材となった木材に60%以上の水分を含有させ、投入
口11より照射室10に投入し、加熱バーナー15を着
火すると、加熱ガスが底部及び周囲を囲繞し、室温が約
150℃に昇温し、遠赤外線放射セラミックス13から
の放射が強くなる。
(Test Example 1) <In the case of construction waste wood and wood waste wood> When waste wood is made to contain 60% or more of water and is put into the irradiation chamber 10 through the inlet 11 and the heating burner 15 is ignited, heating gas is generated. Surrounding the bottom and the periphery, the room temperature rises to about 150 ° C., and the radiation from the far-infrared radiation ceramics 13 becomes strong.

すると、約1時間後に、廃棄物の先ず木質内部の樹液が
遠赤外線放射により赤外活性を示し、共鳴吸収により振
動がエキサイトして分子振幅を大きくし、樹液が気化し
木質部を抜け出して、外部に放散してくる。特に、7〜
14μの波長領域では、樹液に対する赤外活性が強く、
樹液分を有効に気化させることができる。これを、排気
筒19を経て、冷却槽(図示省略)を通して液化させ、
貯留する。これが木酢で、蒸留を加えて処理すれば酢
酸、メチルアルコール、アセトン等の有効成分として利
用できる。
Then, after about 1 hour, the sap inside the wood of the waste first shows infrared activity by far-infrared radiation, and vibration is excited by resonance absorption to increase the molecular amplitude, and the sap vaporizes and escapes from the wood part, Will be released to. Especially 7 ~
In the 14μ wavelength region, the infrared activity against sap is strong,
The sap content can be effectively vaporized. This is liquefied through an exhaust stack 19 and a cooling tank (not shown),
Store. This is wood vinegar, which can be used as an active ingredient such as acetic acid, methyl alcohol, and acetone by treating with distillation.

更に、温度を上昇させ約400℃とし、遠赤外線の照射
を約5時間程度続けると、樹液浸出後の木質部が炭化
し、カーボンとなる。
When the temperature is further raised to about 400 ° C. and irradiation with far-infrared rays is continued for about 5 hours, the wood part after leaching the sap is carbonized to become carbon.

この間、炭化する過程で一部がガス化するので、途中で
切換弁20を作動させて再流管21に導き、加熱バーナ
ー15へ送ると燃料として使用することができ、加熱用
燃料が半分程度に節約される。
During this time, a part is gasified in the process of carbonization, so the switching valve 20 is actuated midway to lead to the reflow pipe 21 and sent to the heating burner 15 so that it can be used as fuel, and about half the heating fuel is used. Is saved.

試験例2 〈電線廃棄物の場合〉 電線廃棄物を約1メートル程度に切断し、これを照射室
10に投入し、約280℃前後で、約4時間遠赤外線放
射セラミックスで照射加熱する。更に燃焼排ガスは石灰
液シャワー槽22を通して、塩素ガスを中性、無害化す
る。
Test Example 2 <In the case of electric wire waste> The electric wire waste is cut into about 1 meter, placed in the irradiation chamber 10, and irradiated and heated with far-infrared radiation ceramics at about 280 ° C for about 4 hours. Further, the combustion exhaust gas passes through the lime liquid shower tank 22 to neutralize chlorine gas and render it harmless.

本法は、二つの面から有利である。その一つは、電線の
周囲を包んだ塩化ビニールは、高温で焼却すると、すぐ
に分解し塩素ガスを放出させる危険があり、炉の損傷を
激しくすると共に公害の原因の一つになっていたが、本
法では比較的低温で処理できるため、塩素ガスの発生は
極小で抑えることができる点にある。
The method is advantageous in two respects. One of the reasons is that the vinyl chloride wrapped around the electric wire may decompose immediately when incinerated at a high temperature and release chlorine gas, which intensifies the damage to the furnace and is one of the causes of pollution. However, in this method, since the treatment can be performed at a relatively low temperature, the generation of chlorine gas can be suppressed to a minimum.

もう一つは、銅及び錫の回収面で効果的であり、つま
り、従来の1300℃程度の焼却をすると、高温のため
銅が硬くなり再生練りの品質が悪化していたが、本法で
は、280℃と低温のため品質の劣化がなく良質の銅が
得られる。又、屋内配線用ケーブル用のFケーブルでは
従来焼却した場合灰の中に錫が落ちてしまい、この灰の
中から錫を再回収する必要があったが、本法では、錫が
落ちることなく銅と同時に回収出来るため、比重選別で
回収できる点にある。
The other is effective in terms of recovering copper and tin. That is, when incineration at about 1300 ° C in the related art, copper becomes hard due to the high temperature and the quality of regenerated kneading deteriorates. Since the temperature is as low as 280 ° C, good quality copper can be obtained without deterioration of quality. In addition, in the case of F cables for indoor wiring cables, when incinerated conventionally, tin fell into the ash, and it was necessary to recover tin from this ash, but with this method, tin does not fall. Since it can be recovered at the same time as copper, it can be recovered by specific gravity selection.

試験例3 〈生ゴミの場合〉 家庭から廃棄される生ゴミや、食品加工場から出るパン
生地を投入し、加熱温度180〜220℃で約4時間照
射処理をする。すると、生ゴミは80%近い水分の含有
があるので、本来蒸発に多量のエネルギーを要するが、
本法では、水分に強い赤外活性があるため、低温でも有
効に吸収が起こり、蒸発を比較的容易に起こすことがで
きる。そして、蒸発後の生ゴミを炭化させることは抑
え、乾燥状態で取り出し、粉砕機で砕いて均一化させた
後、酵素又はバクテイリヤ等を加えて醗酵させ、有機肥
料とする。
Test Example 3 <In the case of raw garbage> Raw garbage discarded from home and bread dough from a food processing plant are put in, and irradiation treatment is performed at a heating temperature of 180 to 220 ° C. for about 4 hours. Then, since garbage contains nearly 80% of water, it takes a lot of energy to evaporate, but
In this method, since infrared rays have a strong infrared activity, effective absorption occurs even at a low temperature, and evaporation can be relatively easily caused. Then, carbonization of the raw garbage after evaporation is suppressed, taken out in a dry state, crushed by a crusher to homogenize, and then fermented by adding an enzyme, a bacterilla or the like to obtain an organic fertilizer.

水産加工廃棄物も同様に処理でき、又、大型家畜の骨や
大型魚類の骨は、魚や動物の飼料とすることもできる。
Fishery processing waste can be treated in the same manner, and the bones of large livestock and the bones of large fish can be used as feed for fish and animals.

試験例4 〈プラスチック廃棄物の場合〉 発泡スチロール、FRP等を照射炉内に投入し、400
℃以内で約1時間照射すると、遠赤外線の照射で一部が
炭化し、これを再流管21を通して加熱バーナー15に
戻しつつ加熱を続けると、最終的に全てがカーボン化す
る。そして、その排気ガスを電線同様に石灰シャワー槽
22を押して、酸化物を回収し、無害化して放出する。
Test Example 4 <In the case of plastic waste> Styrofoam, FRP, etc. were charged into the irradiation furnace and 400
When the irradiation is carried out at a temperature of within 1 ° C. for about 1 hour, a part of the carbonization occurs due to the irradiation of far infrared rays. Then, the exhaust gas is pushed through the lime shower tank 22 in the same manner as the electric wire to recover the oxide, detoxify it, and discharge it.

尚、本法に用いる船舶は遊休船舶を改良して利用するの
が経済的に望ましく、又、洋上処理は船舶を運航させつ
つ、又は、一定箇所に停泊させて行なうの何れでも良
い。そして、本法が廃棄物の海中投棄等を含まないこと
は勿論である。
In addition, it is economically preferable to use an idle ship by improving the ship used in this method, and the offshore treatment may be carried out while the ship is operating or at a fixed location. And, of course, this law does not include the dumping of waste into the sea.

(発明の効果) 以上の構成に基づき本発明は、航行又は停泊する船舶内
で洋上処理できるので、処理用地の確保や住民からの苦
情で難渋するという問題を解消できる実利的効果があ
る。
(Advantages of the Invention) Based on the above configuration, the present invention can perform offshore treatment in a ship that is sailing or moored, so that there is a practical effect that it is possible to solve the problem of securing a treatment site and being difficult due to complaints from residents.

又、遠赤外線を利用した無酸素照射で低温処理できるの
で、燃焼炉の高温と比較してはもとより、従来の乾留炉
と比べても約100℃程度低温で処理でき、廃棄ガスの
発生を抑え、設備の損傷が少なく、且つ、燃焼ガスによ
る大気汚染がないという優れた技術的効果を奏する。
In addition, since it can be processed at low temperature by oxygen-free irradiation using far infrared rays, it can be processed at a low temperature of about 100 ° C compared to the high temperature of a combustion furnace, as well as the temperature of a conventional carbonization furnace, and the generation of waste gas can be suppressed. In addition, there is little technical damage and there is no air pollution due to combustion gas, which is an excellent technical effect.

更に、処理品は木酢や肥料、カーボン等に有効利用でき
るため、焼却して捨てるという従来法の無駄を改めるこ
とができる。
Furthermore, since the treated product can be effectively used as wood vinegar, fertilizer, carbon, etc., the waste of the conventional method of incineration and disposal can be corrected.

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

図面は本発明の実施例を示すもので、第1図は船舶全体
の側面図、第2図は照射炉の模式的側面図。 1・・・船舶 2・・・収納ケース 4・・・遠赤外線
照射炉 6・・・格納庫 10・・・照射室 13・・
・遠赤外線照射セラミックス 14・・・加熱室 15
・・・加熱バーナー 21・・・再流管
The drawings show the embodiments of the present invention. FIG. 1 is a side view of the entire ship, and FIG. 2 is a schematic side view of an irradiation furnace. 1 ... Vessel 2 ... Storage Case 4 ... Far Infrared Irradiation Furnace 6 ... Hangar 10 ... Irradiation Room 13 ...
・ Far infrared irradiation ceramics 14 ・ ・ ・ Heating chamber 15
... Heating burner 21 ... Reflow tube

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】生ゴミ等の都市ゴミ及び漁業廃棄物、水産
加工物、食品加工物、木材加工廃棄物、木材建材廃棄物
等の産業廃棄物の収納ケースを搭載する手段と、 その廃棄物の周囲を遠赤外線放射セラミックスで無酸素
状態に密閉し、且つ、その処理物に適した温度下で遠赤
外線放射を照射加熱して気化及び/又は炭化する加熱手
段を付与すると共に、その熱排気が前記セラミックスの
外側を囲尭する二重層に形成した照射炉と、 該照射処理によって得られた木酢、カーボン等の有効成
分を保管する格納手段とを船舶内に備えたことを特徴と
する廃棄物の処理装置。
1. A means for mounting a storage case for industrial wastes such as municipal wastes such as raw garbage and fishery wastes, fishery products, food products, wood processing wastes, wood building materials wastes, and the wastes. The surroundings are sealed with far-infrared radiation ceramics in an oxygen-free state, and a heating means for irradiating and heating far-infrared radiation at a temperature suitable for the processed material to vaporize and / or carbonize is provided, and its heat exhaust Is disposed in the vessel, the irradiation furnace having a double layer surrounding the outside of the ceramics, and a storage means for storing active ingredients such as wood vinegar and carbon obtained by the irradiation treatment. Object processing equipment.
JP1286889A 1989-11-02 1989-11-02 Waste treatment equipment using ships Expired - Lifetime JPH062274B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1286889A JPH062274B2 (en) 1989-11-02 1989-11-02 Waste treatment equipment using ships

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1286889A JPH062274B2 (en) 1989-11-02 1989-11-02 Waste treatment equipment using ships

Publications (2)

Publication Number Publication Date
JPH03151089A JPH03151089A (en) 1991-06-27
JPH062274B2 true JPH062274B2 (en) 1994-01-12

Family

ID=17710315

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1286889A Expired - Lifetime JPH062274B2 (en) 1989-11-02 1989-11-02 Waste treatment equipment using ships

Country Status (1)

Country Link
JP (1) JPH062274B2 (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100379175B1 (en) * 2000-09-15 2003-04-11 주식회사 지화이브 A carbonizing vessel using far infrared rays and a carbonizing apparatus using the same
KR101129826B1 (en) * 2010-05-20 2012-03-27 타케시 후꾸무라 A carbonization system and the carbonization vehicle for processing all kinds of wastes
CN103801550B (en) * 2014-02-07 2016-08-24 北京中环境盈科技有限公司 Organic waste is smouldered innoxious decrement treatment method
CN103801551A (en) * 2014-02-07 2014-05-21 北京中环境盈科技有限公司 Organic garbage smoulder harmless reduction treatment system
JP6233910B1 (en) * 2016-08-05 2017-11-22 株式会社Sumida Production method of biomass fuel
JP6052649B1 (en) * 2016-08-05 2016-12-27 株式会社Fukutec Indirect heating carbonization system

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5321710A (en) * 1976-08-13 1978-02-28 Nishishiba Denki Kk Brushless synchronous machine rectifier trouble detecting method
US4552082A (en) * 1982-05-27 1985-11-12 Grey Vincent G Offshore incineration of hazardous waste materials
JPH01176486A (en) * 1987-12-28 1989-07-12 Nobuhiko Tomoshige Used syringe disposal method and device

Also Published As

Publication number Publication date
JPH03151089A (en) 1991-06-27

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