JP2006336955A - Method for treating medical waste and facility thereof - Google Patents

Method for treating medical waste and facility thereof Download PDF

Info

Publication number
JP2006336955A
JP2006336955A JP2005163578A JP2005163578A JP2006336955A JP 2006336955 A JP2006336955 A JP 2006336955A JP 2005163578 A JP2005163578 A JP 2005163578A JP 2005163578 A JP2005163578 A JP 2005163578A JP 2006336955 A JP2006336955 A JP 2006336955A
Authority
JP
Japan
Prior art keywords
medical waste
gasification
facility
waste
melting
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
JP2005163578A
Other languages
Japanese (ja)
Inventor
Taro Kusakabe
太郎 日下部
Fumihiro Miyoshi
史洋 三好
Hajime Suzuki
一 鈴木
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.)
JFE Engineering Corp
Original Assignee
JFE Engineering Corp
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 JFE Engineering Corp filed Critical JFE Engineering Corp
Priority to JP2005163578A priority Critical patent/JP2006336955A/en
Publication of JP2006336955A publication Critical patent/JP2006336955A/en
Pending legal-status Critical Current

Links

Images

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
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste
    • 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

  • Apparatus For Disinfection Or Sterilisation (AREA)
  • Processing Of Solid Wastes (AREA)
  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for treating medical waste and facility thereof capable of treating the medical waste safely in an energy-efficient manner. <P>SOLUTION: In the method for treating the medical waste and the facility thereof, a process to accept the medical waste and conduct sterilizing treatment, a process to temporarily store and hold the sterilized medical waste before charging it into a gasification melting facility and a process to mix the stored and held medical waste with other waste and charge them to the gasification melting facility are provided at an installation site of the gasification melting facility at the same time. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、安全にかつエネルギー効率よく、医療系廃棄物を処理可能とする医療系廃棄物の処理方法およびその処理設備に関する。  The present invention relates to a medical waste processing method and a processing facility for the medical waste capable of processing medical waste safely and efficiently.

病院等から発生する医療系廃棄物は、細菌等の感染性物質等を含むことから、専用のコンテナ等の密閉容器(バイオハザードケースと一般に称される)に収納されて焼却炉等によって燃焼処理されることが多い。しかしながら、医療系廃棄物には、メスや注射針等の通常の廃棄物焼却炉では溶融が困難な金属製医療器具等が多く含まれることから、メスや注射針等がその形状を保った状態で焼却灰中に針状のまま残り、危険であった。   Since medical waste generated from hospitals contains infectious substances such as bacteria, it is stored in a closed container (generally called a biohazard case) such as a dedicated container and burned by an incinerator. Often done. However, medical waste contains many metal medical instruments that are difficult to melt in normal waste incinerators such as scalpels and injection needles. In the incineration ash, it remained in a needle shape and was dangerous.

また環廃産発第040316001号(平成16年3月16日)「感染性廃棄物の適正処理について」(http://www.env.go.jp/press/file_view.php3?serial=5741&hou_id=4791)の「4.6 施設内処理」に記載されている、病院等各医療機関で行う高圧蒸気滅菌、煮沸、乾熱滅菌、化学的消毒等の滅菌処理においても、滅菌処理後の注射針、メス等の金属類が鋭利な状態にあるため、搬送時怪我をする危険があった。   In addition, the ring waste production No. 040316001 (March 16, 2004) “Appropriate treatment of infectious waste” (http://www.env.go.jp/press/file_view.php3?serial=5741&hou_id= 4791) “4.6 In-facility treatment”, the injection needle after sterilization even in sterilization such as high-pressure steam sterilization, boiling, dry heat sterilization, chemical disinfection performed in medical institutions such as hospitals There was a risk of injury during transport because of the sharpness of the metal such as the knife.

近年、焼却場における発生ガス中のダイオキシンなど有害物質の管理が問題となっており、高温酸化雰囲気で有害物を分解することが可能な廃棄物焼却設備が開発されてきている。このような高温酸化雰囲気中で廃棄物を処理する廃棄物焼却設備の代表的な例としてガス化溶融設備をあげることができる。
図2に基づき、高温反応炉5を有するガス化溶融設備1について説明する。
In recent years, management of harmful substances such as dioxin in generated gas in incineration has become a problem, and waste incineration equipment capable of decomposing harmful substances in a high-temperature oxidizing atmosphere has been developed. A gasification and melting facility can be given as a typical example of a waste incineration facility that treats waste in such a high-temperature oxidizing atmosphere.
Based on FIG. 2, the gasification melting equipment 1 having the high temperature reactor 5 will be described.

外部から受け入れた廃棄物2は、一旦、ピット3内に堆積された後、クレーン等の廃棄物搬送設備3aによりピット3内からトンネル式加熱炉4の装入口に逐次搬送され、トンネル式加熱炉4に装入される。そして、トンネル式加熱炉4に装入された廃棄物を600 ℃程度に予熱しながら圧縮し、乾燥、熱分解、炭化処理する。鉱物分、金属分を含む廃棄物中、炭化処理で生成した炭化生成物とその熱分解により発生したガス成分は、高温反応炉5内に装入および吹き込まれる。   The waste 2 received from the outside is once deposited in the pit 3 and then sequentially transferred from the pit 3 to the entrance of the tunnel-type heating furnace 4 by the waste transfer equipment 3a such as a crane. 4 is charged. Then, the waste charged in the tunnel-type heating furnace 4 is compressed while preheating to about 600 ° C., dried, pyrolyzed, and carbonized. The carbonized product produced by the carbonization treatment and the gas components generated by the thermal decomposition in the waste containing mineral and metal are charged and blown into the high temperature reactor 5.

高温反応炉5内は、1000℃以上に維持されており、炭化処理で生成した炭化生成物である可燃分は、酸素によって燃焼してガス化する。この際、高温反応炉5内において、吹き込む酸素量を調整することで発生するガスを一酸化炭素と水素を含む燃料用ガスとして回収することができる。また、鉱物分、金属分を含む廃棄物中、炭化不可能な残渣部分は、高温反応炉5内で溶融し、スラグとメタルからなる残渣物6となって高温反応炉5下部から回収される。一方、回収したガスは、急速水冷設備7において多量の水で急冷することでダイオキシン等の生成を防ぎ、ガス精製設備10でガス中の酸、硫黄分等の除去を行い、ガスボイラやガスエンジンの燃料用ガスとする。このようなガス化溶融設備1では、燃料用ガスを用い、発電設備11のガスボイラで高圧蒸気を発生させ、発電機を回転させて発電を行っている。あるいは、発電設備11のガスエンジンで燃料用ガスを燃焼して、発電機を回転させて発電を行っている。   The inside of the high-temperature reactor 5 is maintained at 1000 ° C. or higher, and the combustible component, which is a carbonized product generated by carbonization, is burned by oxygen and gasified. At this time, the gas generated by adjusting the amount of oxygen blown in the high-temperature reactor 5 can be recovered as a fuel gas containing carbon monoxide and hydrogen. In addition, in the waste containing minerals and metals, a residue portion that cannot be carbonized is melted in the high-temperature reactor 5 to be a residue 6 made of slag and metal and recovered from the lower portion of the high-temperature reactor 5. . On the other hand, the recovered gas is rapidly cooled with a large amount of water in the rapid water cooling facility 7 to prevent the formation of dioxins and the like, and the gas purification facility 10 removes acid, sulfur, etc. in the gas, and is used in gas boilers and gas engines. Use as fuel gas. In such a gasification and melting facility 1, fuel gas is used, high pressure steam is generated in the gas boiler of the power generation facility 11, and power is generated by rotating the generator. Alternatively, fuel gas is burned by the gas engine of the power generation facility 11, and the generator is rotated to generate power.

このような構成のガス化溶融設備1では、普通、鉱物分、金属分を含む廃棄物中、炭化可能な物質から可燃ガスを回収することで発電を行っている。その際、急速水冷設備7において除去したガス中のダスト分および水溶成分等は、水処理設備12において除去され、その処理水は、ガス化溶融設備1で再利用される。また、このような構成のガス化溶融設備では、鉱物分、金属分を含む廃棄物中、炭化不可能な残渣部分は、高温反応炉5で溶融され、高温反応炉5の下部から回収される。   In the gasification and melting equipment 1 having such a configuration, power generation is usually performed by recovering a combustible gas from a carbonizable substance in a waste containing minerals and metals. At that time, dust, water-soluble components and the like in the gas removed in the rapid water cooling facility 7 are removed in the water treatment facility 12, and the treated water is reused in the gasification and melting facility 1. Further, in the gasification and melting equipment having such a configuration, in the waste containing minerals and metals, the residual portion that cannot be carbonized is melted in the high temperature reactor 5 and recovered from the lower part of the high temperature reactor 5. .

したがって、医療系廃棄物中、脱脂綿、包帯、紙オムツ等の高カロリーである炭化可能物を原料として使用することにより、ガス化溶融設備のエネルギー効率を高めることが期待できると同時に、医療系廃棄物中、炭化不可能な注射針やメス等の金属製医療器具等は、高温反応炉5で溶融され、メタルとして回収可能であるから、医療系廃棄物の処理として有望であるとされている(特許文献1)。   Therefore, it can be expected to increase the energy efficiency of gasification and melting equipment by using high-calorie carbonized materials such as absorbent cotton, bandages, and paper diapers as raw materials. Metal medical devices such as injection needles and scalpels that cannot be carbonized are melted in the high-temperature reactor 5 and can be recovered as metal, and thus are considered promising as a treatment for medical waste. (Patent Document 1).

特許文献1には、ガス化溶融設備を用い、医療系廃棄物を含む廃棄物を回分的に加圧、圧縮する工程と、得られた圧縮成型物をトンネル式加熱炉内に装入し、乾燥、熱分解、炭化する工程と、得られた炭化生成物を高温反応器内に装入し、燃焼して不燃分を溶融する工程を有する廃棄物処理設備が開示されている。この特許文献1に記載の医療系廃棄物の処理技術は、ガス化溶融設備のトンネル式加熱炉内へバイオハザードケースごと、医療系廃棄物を装入する方法を採用している。
特開平11-218313 号公報
In Patent Document 1, using a gasification melting facility, batchwise pressurizing and compressing waste including medical waste, and charging the obtained compression molding into a tunnel-type heating furnace, A waste treatment facility having a process of drying, pyrolysis and carbonization, and a process of charging the obtained carbonized product into a high-temperature reactor and combusting to melt non-combustible components is disclosed. The medical waste treatment technology described in Patent Document 1 employs a method of charging medical waste into the tunnel heating furnace of a gasification and melting facility for each biohazard case.
Japanese Patent Laid-Open No. 11-218313

しかしながら、特許文献1に記載の医療系廃棄物の処理方法では、医療系廃棄物を収めた密封容器であるバイオハザードケースごと、トンネル式加熱炉に装入することから、炉内のガスの外部への飛散を避けるために2段のシール弁を有する投入装置を用意し、この投入装置を用いて容器を一つ一つ順にトンネル式加熱炉内へ装入するといった手間が必要であることや、また、確実なシールを行うために、投入装置のシール弁構造を堅固な作りとすることが必要であることから、設備費、メンテナンス費が高くなるという問題があった。そのため、従来のガス化溶融設備を改造して特許文献1に開示の処理工程とするまでには至らないのが現状である。   However, in the method for treating medical waste described in Patent Document 1, the biohazard case, which is a sealed container containing medical waste, is inserted into a tunnel-type heating furnace, so that the outside of the gas in the furnace In order to avoid scattering, it is necessary to prepare a charging device with a two-stage seal valve and use this charging device to load the containers one by one into the tunnel furnace. In addition, in order to perform reliable sealing, it is necessary to make the sealing valve structure of the charging device firm, so there is a problem that the equipment cost and the maintenance cost become high. Therefore, the current situation is that the conventional gasification melting equipment is not remodeled to the processing process disclosed in Patent Document 1.

一方、医療系廃棄物をガス化溶融設備に装入する前に、各地に分散している病院等の医療機関等がそれぞれ、医療系廃棄物の滅菌処理を行い、その後、滅菌処理した医療系廃棄物をガス化溶融設備に搬送するようにすれば、特許文献1のような特別の設備が不要となり、従来のガス化溶融設備をそのまま適用できる可能性がある。しかし、そのためには、各地に分散している病院等の医療機関毎に、オートクレーブと称されるような医療系廃棄物の滅菌処理設備を設ける必要が生じ、そうすると、滅菌処理設備の稼働率が上がらず、加熱して滅菌処理するエネルギーも医療機関毎に必要となるため、非常にエネルギー効率が悪かった。図3に従来の医療系廃棄物20の処理フローを示す。   On the other hand, before charging medical waste into gasification and melting equipment, medical institutions such as hospitals dispersed in various places sterilize medical waste, and then sterilize the medical waste. If the waste is transported to the gasification and melting equipment, the special equipment as in Patent Document 1 is not necessary, and the conventional gasification and melting equipment may be applied as it is. However, in order to do so, it is necessary to provide a medical waste sterilization facility called an autoclave for each medical institution such as a hospital distributed in various places. The energy efficiency of heating and sterilization is not required for each medical institution, so the energy efficiency is very poor. FIG. 3 shows a processing flow of the conventional medical waste 20.

従来の医療系廃棄物20の処理工程は、病院等の医療機関40毎に、滅菌処理設備15で滅菌処理する工程を行い、滅菌処理した医療系廃棄物20をバイオハザードケースに収納した後、一般廃棄物30とともに一緒に回収工程50 で回収し、その後、廃棄物処理設備に装入する工程とされている。このような従来の医療系廃棄物20の処理工程では、医療系廃棄物20がプラスチック製や金属製のバイオハザードケースに収納された状態で廃棄物処理設備に装入されていたので、回収される燃料ガスの発熱量が大きく変動することもあった。このため、医療系廃棄物を処理するために炉全体の廃棄物処理量が低下した。また高カロリーのバイオハザードケースを処理した場合、耐火物を損傷する等の問題があった。   The conventional treatment process of medical waste 20 is performed for each medical institution 40 such as a hospital by performing a sterilization process in the sterilization equipment 15, and after storing the sterilized medical waste 20 in a biohazard case, It is set as the process of collect | recovering together with the general waste 30 by the collection | recovery process 50, and charging with a waste disposal facility after that. In such a conventional treatment process for medical waste 20, since the medical waste 20 was stored in a plastic or metal biohazard case and was loaded into a waste treatment facility, it was collected. The amount of heat generated by the fuel gas may fluctuate greatly. For this reason, in order to process medical waste, the waste processing amount of the whole furnace fell. Moreover, when a high calorie biohazard case was processed, there existed problems, such as refractory being damaged.

またさらに、従来の医療系廃棄物20の処理工程では、各地に分散している病院等の医療機関40毎に、滅菌処理設備15で加熱して殺菌処理する際に発生する滅菌処理使用後の水も処理する必要が生じるため、この滅菌処理使用後の水を処理するための水処理エネルギー、及び水処理設備が新たに必要となるという問題もあった。
本発明は、上記の課題を解決し、安全にかつエネルギー効率よく、医療系廃棄物を処理可能とする医療系廃棄物処理方法および設備を提供するものである。
Furthermore, in the conventional treatment process of medical waste 20, after the use of sterilization treatment that occurs when sterilization treatment is performed in the sterilization equipment 15 for each medical institution 40 such as a hospital dispersed in various places. Since it is also necessary to treat water, there is a problem that water treatment energy and water treatment equipment for treating water after use of this sterilization treatment are newly required.
The present invention provides a medical waste treatment method and facility that solves the above-described problems and enables safe and energy-efficient treatment of medical waste.

本発明は、以下のとおりである。
1. 廃棄物のガス化溶融設備を用いた医療系廃棄物の処理方法であって、前記医療系廃棄物を受け入れて滅菌処理する工程と、該滅菌処理した医療系廃棄物をガス化溶融設備へ装入する前に一旦貯留保持する工程と、該貯留保持した医療系廃棄物を他の廃棄物と混合して前記ガス化溶融設備に装入する工程とを、前記ガス化溶融設備の設置場所に同時に有するようにしたことを特徴とする医療系廃棄物の処理方法。
The present invention is as follows.
1. A method of treating medical waste using a waste gasification and melting facility, the step of receiving and sterilizing the medical waste, and installing the sterilized medical waste into the gasification and melting facility. A step of temporarily storing and holding before entering, and a step of mixing the stored medical waste with other waste and charging it into the gasification and melting equipment at the installation location of the gasification and melting equipment. A method for treating medical waste, characterized in that it has at the same time.

2.前記ガス化溶融設備に装入する工程において、回収される燃料ガスの発熱量に応じて、医療系廃棄物の装入割合を調整して前記ガス化溶融設備で医療系廃棄物を処理することを特徴とする上記1.に記載の医療系廃棄物の処理方法。
3.前記ガス化溶融設備で発生したエネルギーの一部を利用して前記医療系廃棄物の滅菌処理を行うように構成して前記ガス化溶融設備で医療系廃棄物を処理するようにしたことを特徴とする上記1.又は2.に記載の医療系廃棄物の処理方法。
2. In the step of charging into the gasification and melting equipment, the medical waste is processed in the gasification and melting equipment by adjusting the charging rate of the medical waste according to the calorific value of the recovered fuel gas. 1 characterized by the above. A method for treating medical waste as described in 1. above.
3. The medical waste is sterilized using a part of the energy generated in the gasification and melting equipment, and the medical waste is processed in the gasification and melting equipment. The above 1. Or 2. A method for treating medical waste as described in 1. above.

4.前記医療系廃棄物の滅菌処理を蒸気により行うように構成するとともに、前記蒸気が凝縮して生じた滅菌処理使用後の水を前記ガス化溶融設備の水処理設備で処理するようにしたことを特徴とする上記1.〜3.のいずれかに記載の医療系廃棄物の処理方法。
5.前記医療系廃棄物を受け入れて滅菌処理する工程と、前記ガス化溶融設備に装入する工程とを相互補完的に行って前記ガス化溶融設備で医療系廃棄物を処理することを特徴とする上記1.〜4.のいずれかに記載の医療系廃棄物の処理方法。
4). The medical waste is configured to be sterilized by steam, and the water after use of the sterilization generated by condensation of the steam is treated by the water treatment facility of the gasification melting facility. Characteristic 1. ~ 3. A method for treating medical waste according to any one of the above.
5. The medical waste is treated in the gasification and melting equipment by mutually complementing the step of receiving and sterilizing the medical waste and the step of charging into the gasification and melting equipment. Above 1. ~ 4. A method for treating medical waste according to any one of the above.

6.前記医療系廃棄物中に金属製医療器具を含み、該金属製医療器具の金属分を溶融処理し、メタルとして回収しつつ、前記ガス化溶融設備で医療系廃棄物を処理することを特徴とする上記1.〜5.のいずれかに記載の医療系廃棄物の処理方法。
7.廃棄物のガス化溶融設備を用いた医療系廃棄物の処理装置であって、前記ガス化溶融設備には、受け入れた医療系廃棄物を滅菌処理する滅菌処理設備と、該滅菌処理設備で滅菌処理した医療系廃棄物を前記滅菌処理設備へ装入する前に一旦貯留保持するピットと、該ピットで貯留保持した医療系廃棄物を他の廃棄物と混合して混合廃棄物として貯留保持するピットと、該混合廃棄物を前記ガス化溶融設備に装入する廃棄物搬送設備と、が近接配置され、前記滅菌処理設備が、前記ガス化溶融設備で発生したエネルギーの一部を利用して前記医療系廃棄物の滅菌処理を行うことが可能なように前記ガス化溶融設備の発電設備と接続されていることを特徴とする医療系廃棄物の処理設備。
6). A metal medical instrument is included in the medical waste, the metal waste of the metal medical instrument is melted and recovered as metal, and the medical waste is processed in the gasification melting facility. 1 above. ~ 5. A method for treating medical waste according to any one of the above.
7). A medical waste processing apparatus using a waste gasification and melting equipment, wherein the gasification and melting equipment includes a sterilization equipment for sterilizing received medical waste, and sterilization by the sterilization equipment. Prior to charging the treated medical waste into the sterilization facility, the pit is temporarily stored and held, and the medical waste stored and held in the pit is mixed with other waste and stored as mixed waste. A pit and a waste transport facility for charging the mixed waste into the gasification and melting facility are arranged close to each other, and the sterilization facility uses a part of the energy generated in the gasification and melting facility. A treatment facility for medical waste, wherein the treatment facility is connected to a power generation facility of the gasification and melting facility so that the medical waste can be sterilized.

8.前記滅菌処理設備が、前記ガス化溶融設備の発電設備で用いる蒸気を発生させるガスボイラと蒸気配管で接続されているとともに、前記ガス化溶融設備の水処理設備と滅菌処理使用後の水を搬送する排水配管で接続されていることを特徴とする上記7.に記載の医療系廃棄物の処理設備。   8). The sterilization equipment is connected to a gas boiler that generates steam used in the power generation equipment of the gasification and melting equipment and a steam pipe, and transports water after use of the sterilization processing and the water treatment equipment of the gasification and melting equipment. 6. It is connected with a drain pipe. Medical waste treatment facility as described in 1.

本発明によれば、各地に分散している病院等の医療機関毎に、滅菌処理設備を設置する必要がなくなり、廃棄物のカロリーの安定化にともない処理量を定格フルで使用でき、医療系廃棄物をガス燃料として利用が可能となり、炉体への熱負荷が低減され、耐火物の延命が可能となった。また、滅菌処理設備で使用するエネルギーをガス化溶融設備から供給できるから、安全にかつエネルギー効率よく、医療系廃棄物を処理することができる。   According to the present invention, it is not necessary to install a sterilization treatment facility for each medical institution such as a hospital dispersed in various places, and the treatment amount according to stabilization of the calories of waste can be used at a full rating. Waste can be used as gas fuel, the heat load on the furnace body is reduced, and the life of refractories can be extended. In addition, since the energy used in the sterilization facility can be supplied from the gasification and melting facility, medical waste can be treated safely and efficiently.

本発明の実施の形態にかかる医療系廃棄物の処理設備の構成を図1に示す。
図1は、本発明の実施の形態にかかる医療系廃棄物の処理設備の構成を示す模式図である。図1中、図2において既に説明した従来のガス化溶融設備1と同一のものには同一符号を付し、ガス化溶融設備1についての再度の説明を省略する。
なお、受け入れた医療系廃棄物20に滅菌処理を行うには、種々の方式があるが、ここでは、蒸気滅菌オートクレーブ方式の滅菌処理設備15をガス化溶融設備1の機側に近接して設置した場合を例として説明する。また、ピット3には、滅菌処理した医療系廃棄物20をガス化溶融設備1へ装入する前に、一旦貯留保持するピットと、貯留保持した医療系廃棄物20をその他の一般廃棄物30と混合して混合廃棄物30Aとして貯留保持するピットとを新たに付帯させた。
FIG. 1 shows the configuration of a medical waste treatment facility according to an embodiment of the present invention.
FIG. 1 is a schematic diagram showing a configuration of a medical waste treatment facility according to an embodiment of the present invention. In FIG. 1, the same components as those of the conventional gasification and melting equipment 1 already described in FIG. 2 are denoted by the same reference numerals, and the description of the gasification and melting equipment 1 is omitted.
There are various methods for sterilizing the received medical waste 20, but here, a steam sterilization autoclave sterilization facility 15 is installed close to the gasification and melting facility 1. This will be described as an example. Also, in the pit 3, before the sterilized medical waste 20 is charged into the gasification and melting facility 1, the pit that temporarily stores and holds the medical waste 20 that has been stored and held in the other general waste 30. And a pit to be stored and retained as mixed waste 30A.

すなわち、図1に示すように、ピット3の構造は、隔壁で隔てられた3槽とされ、トンネル式加熱炉4の装入口に最も近い槽が従来から設置されている一般廃棄物30を貯留保持するピットであり、トンネル式加熱炉4の装入口から最も離れた槽が滅菌処理設備15で滅菌処理した医療系廃棄物20を一旦貯留保持するピットであり、その中間の槽が、滅菌処理した医療系廃棄物20をガス化溶融設備1へ装入する前に、その他の一般廃棄物30と混合して混合廃棄物30Aとして貯留保持するピットである。ここで、滅菌処理した医療系廃棄物20を一旦貯留保持するピット、及び混合廃棄物30Aとして貯留保持するピットには、攪拌装置を設置して、医療系廃棄物20をガス化溶融設備1へ装入する前に、攪拌することがよりカロリーの均一化を図ることができるので好ましい。また、ガス化溶融設備1へ装入する前に、滅菌処理した医療系廃棄物20を一旦貯留保持する理由は、バイオハザードケースごとに収納された医療系廃棄物20のカロリーが異なっているので、受け入れた医療系廃棄物20をバイオハザードケースから取り出し、滅菌処理した医療系廃棄物20をピット内に貯留保持して、ガス化溶融設備1へ装入する前に、医療系廃棄物20のカロリーの均一化を図るためである。   That is, as shown in FIG. 1, the structure of the pit 3 is made up of three tanks separated by a partition wall, and the general waste 30 in which the tank closest to the inlet of the tunnel-type heating furnace 4 is conventionally stored is stored. The pit to hold, the tank farthest from the inlet of the tunnel-type heating furnace 4 is the pit that temporarily stores and holds the medical waste 20 sterilized by the sterilization equipment 15, and the tank in the middle is sterilized. This is a pit that is mixed with other general waste 30 and stored as mixed waste 30A before charging the medical waste 20 into the gasification and melting facility 1. Here, in the pit for temporarily storing and holding the sterilized medical waste 20 and the pit for storing and holding the mixed waste 30A, a stirrer is installed to transfer the medical waste 20 to the gasification and melting facility 1. It is preferable to stir before charging since the calorie can be made more uniform. Moreover, the reason why the sterilized medical waste 20 is once stored and held before charging into the gasification and melting equipment 1 is that the calorie of the medical waste 20 stored for each biohazard case is different. Take out the received medical waste 20 from the biohazard case, store and hold the sterilized medical waste 20 in the pit, and insert it into the gasification and melting facility 1 before the medical waste 20 This is to make the calories uniform.

医療系廃棄物20の処理をガス化溶融設備1で行う際には、クレーン等の廃棄物搬送設備3aで、カロリーの均一化を図った混合廃棄物30Aをピット3から所定量持ち上げ、トンネル式加熱炉4の装入口の上方にまで搬送して、その位置でトンネル式加熱炉4の装入口に装入する。このようにして、ガス化溶融設備1に装入された廃棄物をトンネル式加熱炉4で100〜600 ℃に予熱しながら圧縮し、乾燥、熱分解、炭化処理する。鉱物分、金属分を含む廃棄物中、炭化処理で生成した炭化生成物とその熱分解により発生したガス成分は、高温反応炉5内に装入および吹き込まれるのは従来の廃棄物処理工程と同様である。   When the medical waste 20 is processed in the gasification and melting facility 1, the waste transport facility 3a such as a crane lifts a predetermined amount of the mixed waste 30A from which the calories are uniformed from the pit 3 and tunnel type. It conveys to the upper part of the inlet of the heating furnace 4, and is inserted into the inlet of the tunnel heating furnace 4 at that position. In this way, the waste charged in the gasification and melting facility 1 is compressed in the tunnel heating furnace 4 while preheating to 100 to 600 ° C., and dried, pyrolyzed, and carbonized. Among wastes containing minerals and metals, carbonized products produced by carbonization and gas components generated by thermal decomposition thereof are charged and blown into the high-temperature reactor 5 according to the conventional waste treatment process. It is the same.

この本発明の実施の形態にかかる医療系廃棄物の処理設備は、蒸気滅菌オートクレーブ方式の滅菌処理設備15が、ガス化溶融設備1の発電設備11で用いる蒸気を発生させるガスボイラと蒸気配管16で接続されているとともに、ガス化溶融設備1の水処理設備12と滅菌処理使用後の水を搬送する排水配管17で接続されている。
すなわち、本発明の実施の形態に係る医療系廃棄物の処理設備は、従来のガス化溶融設備1(図2参照)に対して、受け入れた医療系廃棄物20を滅菌処理する滅菌処理設備15と、滅菌処理設備15で滅菌処理した医療系廃棄物20をガス化溶融炉1へ装入する前に、一旦貯留保持するピットと、該ピットで貯留保持した医療系廃棄物20をその他の一般廃棄物30と混合して混合廃棄物30Aとして貯留保持するピットと、該混合廃棄物30Aを前記ガス化溶融設備に装入する廃棄物搬送設備3aとが、近接配置され、滅菌処理設備15がガス化溶融設備1で発生したエネルギーの一部を利用して医療系廃棄物20の滅菌処理を行うように構成されている。このため、医療系廃棄物20の処理を行う際には、蒸気を用いて発電する発電設備11のエネルギーの一部を滅菌処理設備15で使用できるとともに、蒸気滅菌オートクレーブ方式の滅菌処理設備15がガス化溶融設備1の水処理設備12と排水配管17で接続されているので、滅菌処理使用後の水を排水配管17により搬送して水処理設備12で処理できる。
このガス化溶融設備1を用いた医療系廃棄物の処理方法では、受け入れた医療系廃棄物20に対して以下のようにして医療系廃棄物20を処理することができる。
The medical waste processing facility according to the embodiment of the present invention includes a steam sterilization autoclave sterilization facility 15 that includes a gas boiler and a steam pipe 16 that generate steam used in the power generation facility 11 of the gasification and melting facility 1. In addition to being connected, it is connected to the water treatment facility 12 of the gasification and melting facility 1 by a drain pipe 17 that carries water after sterilization treatment.
That is, the medical waste processing facility according to the embodiment of the present invention is a sterilization processing facility 15 for sterilizing the received medical waste 20 with respect to the conventional gasification melting facility 1 (see FIG. 2). Before the medical waste 20 sterilized by the sterilization processing facility 15 is charged into the gasification melting furnace 1, the pit once stored and held, and the medical waste 20 stored and held in the pit by other general A pit that is mixed with the waste 30 and stored and retained as a mixed waste 30A, and a waste transport facility 3a that charges the mixed waste 30A into the gasification and melting facility are arranged close to each other, and the sterilization processing facility 15 is provided. The medical waste 20 is sterilized by using a part of the energy generated in the gasification melting facility 1. For this reason, when the medical waste 20 is treated, a part of the energy of the power generation equipment 11 that generates power using steam can be used in the sterilization equipment 15, and the sterilization equipment 15 of the steam sterilization autoclave system is used. Since the water treatment equipment 12 of the gasification and melting equipment 1 is connected to the drainage pipe 17, the water after sterilization treatment can be transported through the drainage pipe 17 and processed by the water treatment equipment 12.
In the medical waste processing method using the gasification and melting equipment 1, the medical waste 20 can be processed with respect to the received medical waste 20 as follows.

蒸気滅菌オートクレーブ方式の滅菌処理設備15では、医療系廃棄物20をオートクレーブ中に所定量投入した後、オートクレーブ内の空気を排出して低圧化し、その中に130 ℃を超える程度の加圧蒸気を送給することで滅菌処理を行う。その際、滅菌処理設備15で使用する高温の蒸気の全ては、蒸気配管16を経由して発電設備11のガスボイラで発生させた高圧蒸気から送給される。その後、オートクレーブ内の蒸気を排気し、滅菌後の廃棄物をある程度、ガスボイラから供給されたエネルギーを用いて乾燥させてから、オートクレーブを開いて滅菌処理した医療系廃棄物20を取り出して1サイクルの滅菌処理する工程が終了する。その際、排気した蒸気は、コンデンサで再び水に凝縮され、滅菌処理使用後の水を排水配管17により搬送して水処理設備12に送給され、ガス化溶融設備1の急速水冷設備7で使用する冷却水等と一緒に水処理設備12で処理された滅菌処理使用後の水は、ガス化溶融設備1の急速水冷設備7などで有効利用される。なお、説明するまでもないが、蒸気滅菌オートクレーブ方式の滅菌処理設備15で使用する高温、高圧の蒸気は、医療系廃棄物中、脱脂綿、包帯、紙オムツ等の高カロリーである炭化可能物を原料として、高温反応炉5内において、吹き込む酸素量を調整することで発生させた一酸化炭素と水素を含むガスを、急速水冷設備7において多量の水で急冷することでダイオキシン等の生成を防ぎつつ、ガス精製設備10でガス中の酸、硫黄分等の除去を行って回収した燃料用ガスを、発電設備11のガスボイラで燃焼させて発生させた蒸気の一部である。   In the steam sterilization autoclave-type sterilization equipment 15, after a predetermined amount of medical waste 20 is put into the autoclave, the air in the autoclave is discharged to reduce the pressure, and pressurized steam exceeding 130 ° C is contained therein. Sterilization is performed by feeding. At that time, all of the high-temperature steam used in the sterilization facility 15 is supplied from the high-pressure steam generated in the gas boiler of the power generation facility 11 via the steam pipe 16. After that, the steam in the autoclave is evacuated, and the sterilized waste is dried to some extent using the energy supplied from the gas boiler. Then, the autoclave is opened, and the sterilized medical waste 20 is taken out for one cycle. The sterilization process is completed. At that time, the exhausted steam is condensed again into water by a condenser, and the water after sterilization treatment is transported through the drain pipe 17 to be supplied to the water treatment facility 12, and is supplied to the rapid water cooling facility 7 of the gasification melting facility 1. The sterilized water used in the water treatment facility 12 together with the cooling water to be used is effectively used in the rapid water cooling facility 7 of the gasification and melting facility 1 or the like. Needless to say, high-temperature, high-pressure steam used in the steam sterilization autoclave sterilization equipment 15 is a high-calorie carbonized material such as absorbent cotton, bandages, paper diapers, etc. in medical waste. As a raw material, dioxins are prevented from being generated by quenching a gas containing carbon monoxide and hydrogen generated by adjusting the amount of oxygen blown in the high-temperature reactor 5 with a large amount of water in the rapid water-cooling facility 7. On the other hand, it is a part of the steam generated by burning the fuel gas recovered by removing the acid, sulfur, etc. in the gas with the gas purification facility 10 in the gas boiler of the power generation facility 11.

このように、ガス化溶融設備1を用いた医療系廃棄物の処理方法は、医療系廃棄物20を受け入れて滅菌処理する工程と、滅菌処理した医療系廃棄物20をガス化溶融設備1へ装入する前に一旦貯留保持する工程と、貯留保持した医療系廃棄物20を他の廃棄物と混合してガス化溶融設備1に装入する工程とを、ガス化溶融設備1の設置場所に同時に有するとともに、ガス化溶融設備1で発生したエネルギーの一部を利用して医療系廃棄物20の滅菌処理を行う処理方法である。   As described above, the medical waste processing method using the gasification and melting equipment 1 includes the step of receiving the medical waste 20 and sterilizing, and the sterilized medical waste 20 to the gasification and melting equipment 1. The installation location of the gasification and melting equipment 1 includes the step of temporarily storing and holding before charging, and the step of mixing the stored medical waste 20 with other waste and charging it into the gasification and melting equipment 1. And a sterilization treatment of the medical waste 20 using a part of the energy generated in the gasification melting facility 1.

従って、本発明の実施の形態に係る医療系廃棄物の処理装置及び処理方法によれば、各地に分散している病院等の医療機関毎に、滅菌処理設備および滅菌処理使用後の水処理設備を設置する必要がなくなり、安全にかつエネルギー効率よく、医療系廃棄物を処理することができる。また、廃棄物のガス化溶融設備1を用いた医療系廃棄物の処理方法によれば、廃棄物のトータル処理システムとしても、エネルギーの効率化が達成できる。   Therefore, according to the medical waste processing apparatus and processing method according to the embodiment of the present invention, for each medical institution such as a hospital distributed in various places, sterilization processing equipment and water processing equipment after use of sterilization processing The medical waste can be treated safely and energy-efficiently. In addition, according to the medical waste processing method using the waste gasification and melting facility 1, energy efficiency can be achieved even as a total waste processing system.

ところで、滅菌処理設備15としては、高温、高圧の蒸気を用いた蒸気滅菌オートクレーブ方式の他に、加熱殺菌方式として、マイクロ波を用いたマイクロ波滅菌方式や、熱風加熱による乾熱滅菌方式でもよいことは言うまでもない。その場合、受け入れた医療系廃棄物20の滅菌処理に使用するエネルギーとしては、ガス化溶融設備1の発電設備11で発電して得た電気エネルギーを用いることになる。このため、加熱殺菌方式として、電気エネルギーを用いる滅菌方式の滅菌処理設備の場合には、滅菌処理設備と発電設備11とを蒸気配管16で接続する代わりに、発電設備11と滅菌処理設備とを電源ケーブルで接続する。なお、マイクロ波を用いたマイクロ波滅菌方式や、熱風加熱による乾熱滅菌方式の滅菌処理設備の場合には、図1に示したような、滅菌処理使用後の水を水処理設備12に送給するための排水配管17は設ける必要がない。   By the way, as the sterilization processing equipment 15, in addition to the steam sterilization autoclave method using high-temperature and high-pressure steam, the heat sterilization method may be a microwave sterilization method using microwaves or a dry heat sterilization method using hot air heating. Needless to say. In that case, as the energy used for the sterilization treatment of the received medical waste 20, the electric energy obtained by the power generation facility 11 of the gasification melting facility 1 is used. For this reason, in the case of a sterilization treatment facility using electrical energy as a heat sterilization method, instead of connecting the sterilization treatment facility and the power generation facility 11 with the steam pipe 16, the power generation facility 11 and the sterilization treatment facility are connected. Connect with the power cable. In the case of a sterilization treatment facility using a microwave or a dry heat sterilization method using hot air heating, the water after sterilization use as shown in FIG. It is not necessary to provide the drain pipe 17 for supplying.

ここで、蒸気滅菌オートクレーブ方式の滅菌処理設備15をガス化溶融設備1の機側に設置し、蒸気滅菌オートクレーブ方式の滅菌処理設備15が、ガス化溶融設備1の発電設備11で用いる蒸気を発生させるガスボイラと蒸気配管16で接続されているとともに、ガス化溶融設備1の水処理設備12と滅菌処理使用後の水を搬送する排水配管17で接続されている医療系廃棄物の処理設備とするのが好ましい。   Here, a steam sterilization autoclave sterilization equipment 15 is installed on the gasification and melting equipment 1 side, and the steam sterilization autoclave sterilization equipment 15 generates steam to be used in the power generation equipment 11 of the gasification and melting equipment 1. It is connected to the gas boiler and the steam pipe 16 to be used, and the medical waste treatment equipment is connected to the water treatment equipment 12 of the gasification and melting equipment 1 and the drainage pipe 17 for transporting the sterilized water after use. Is preferred.

この理由は、高温、高圧の蒸気を用いた蒸気滅菌オートクレーブ方式の滅菌処理設備をガス化溶融設備1の機側に設置した場合と、電気エネルギーを用いる滅菌方式の滅菌処理設備をガス化溶融設備1の機側に設置した場合とを比較すると、発電設備11で発電した電気に比べて発電設備11で使用する蒸気の方がエネルギーコストが安価であることから、医療系廃棄物20の滅菌処理を蒸気により行うように構成するとともに、蒸気が凝縮して生じた滅菌処理使用後の水をガス化溶融設備1の水処理設備12に搬送して、水処理設備12で処理するようにした方が用役費が安価となるからである。   The reason for this is that a steam sterilization autoclave sterilization facility using high-temperature, high-pressure steam is installed on the machine side of the gasification melting facility 1 and a sterilization sterilization facility using electric energy is gasification melting facility. Compared with the case where it is installed on the machine 1 side, the energy cost of steam used in the power generation equipment 11 is lower than that of electricity generated by the power generation equipment 11, so the sterilization treatment of the medical waste 20 In which water is used for sterilization treatment, which is generated by condensation of steam, and is transported to the water treatment facility 12 of the gasification and melting facility 1 for treatment by the water treatment facility 12 This is because the utility cost is low.

また、ガス化溶融設備1に装入する工程において、回収される燃料ガスの発熱量に応じて、医療系廃棄物20の装入割合を調整してガス化溶融設備1で医療系廃棄物を処理することが好ましい。この理由は、医療系廃棄物20には、脱脂綿、包帯、紙オムツ等の高カロリーでかつ低灰分である炭化可能物から使用後の注射針、メス等の低カロリーでかつ高灰分である炭化不可能物まで含まれている。そこで、ガス化溶融設備1へ装入する前に、滅菌処理した医療系廃棄物20をピット内に一旦貯留保持することで、バイオハザードケースごとに異なるカロリーは均一化されるが、高温部分でも固体として存在する固定炭素の量が灰分の量と比較して少ない場合がある。医療系廃棄物20以外の一般廃棄物30の固定炭素、灰分との合計で調整する必要があり、このため、貯留保持した医療系廃棄物20をその他の一般廃棄物30と混合する際に、回収される燃料ガスの発熱量に応じて、医療系廃棄物20の装入割合を調整するのが好ましい。   Further, in the process of charging the gasification and melting facility 1, the charging rate of the medical waste 20 is adjusted according to the heat generation amount of the recovered fuel gas, and the medical waste is discharged by the gasification and melting facility 1. It is preferable to process. The reason for this is that the medical waste 20 is carbonized with a high calorie and low ash content such as absorbent cotton, bandages, paper diapers, etc. The impossible is included. Therefore, by storing and holding the sterilized medical waste 20 once in the pit before charging into the gasification and melting facility 1, the calories that differ for each biohazard case are made uniform. The amount of fixed carbon present as a solid may be small compared to the amount of ash. It is necessary to adjust the total of fixed carbon and ash of general waste 30 other than medical waste 20, so when mixing stored medical waste 20 with other general waste 30, It is preferable to adjust the charging rate of the medical waste 20 according to the heat value of the recovered fuel gas.

また、ガス化溶融設備1を用いた医療系廃棄物の処理方法では、医療系廃棄物20を受け入れて滅菌処理する工程と、ガス化溶融設備1に装入する工程とを相互補完的に行ってガス化溶融設備1で医療系廃棄物を処理することが、回収される燃料ガスの発熱量をより均一にできるので好ましい。
また、医療系廃棄物20には、使用後の注射針、メス等が多く含まれている。そこで、ガス化溶融設備1を用いた医療系廃棄物の処理方法では、医療系廃棄物中の金属分を溶融処理し、メタルとして回収しつつ、前記ガス化溶融設備1で医療系廃棄物を処理することが、高温反応炉5下部から回収する残渣物6の処理が容易となるので好ましい。そのためには、ガス化溶融設備1の高温反応炉5内の温度を1600℃以上に維持して、使用後の注射針、メス等の金属分を高温反応炉5内で溶融し、メタルとして高温反応炉5下部からスラグと一緒に回収するようにする。ここで、ガス化溶融設備1の高温反応炉5内の温度が1600℃未満となると、医療系廃棄物中の金属分を溶融することができない場合が発生し、溶融されず残った注射針、メス等により怪我をする危険があるため、スラグと一緒に残った残渣物6の処理に困るためである。
In the medical waste treatment method using the gasification and melting equipment 1, the process of receiving the medical waste 20 and sterilizing and the process of charging the gasification and melting equipment 1 are performed in a complementary manner. Therefore, it is preferable to treat the medical waste in the gasification and melting equipment 1 because the calorific value of the recovered fuel gas can be made more uniform.
In addition, the medical waste 20 contains many used injection needles, scalpels, and the like. Therefore, in the method for treating medical waste using the gasification and melting equipment 1, the metal content in the medical waste is melted and recovered as metal, while the medical waste is collected in the gasification and melting equipment 1. It is preferable to treat the residue 6 because the residue 6 collected from the lower part of the high temperature reactor 5 can be easily treated. For this purpose, the temperature in the high-temperature reactor 5 of the gasification and melting equipment 1 is maintained at 1600 ° C. or higher, and metal components such as used needles and scalpels are melted in the high-temperature reactor 5 to obtain a high temperature as metal. It collect | recovers with slag from the reactor 5 lower part. Here, when the temperature in the high-temperature reactor 5 of the gasification melting equipment 1 is less than 1600 ° C., there is a case where the metal content in the medical waste cannot be melted, and the remaining injection needle that is not melted. This is because there is a risk of injury from a scalpel or the like, and it is difficult to process the residue 6 remaining together with the slag.

ここでは、図1に示すガス化溶融設備1の機側に蒸気滅菌オートクレーブ方式の滅菌処理設備15を近接配置して、ガス化溶融設備1で医療系廃棄物20の処理を行った実施例について説明する。ガス化溶融設備1は、廃棄物を9t/h処理可能であり、高温反応炉5において6t/hの酸素を供給することで10t/hの燃料ガスを製造することができる。そして、この燃料ガスを利用するガスボイラによって7t/hの高圧蒸気を発生でき、発電設備11で発電に使用している。また、ガス化溶融設備1の水処理設備は4t/hの環水を処理できる。本実施例では、医療系廃棄物20を受け入れて、滅菌処理設備15で、1サイクル当たり、約250 kg高圧蒸気を用いて、滅菌処理温度を135 ℃とし、4m3 の医療系廃棄物(約1〜2tに相当)を約1時間で滅菌処理した。その際、ガス化溶融設備1へ装入する前に、医療系廃棄物20の滅菌処理を発電設備11のガスボイラで発生させた高圧蒸気の一部を利用して行った。また、医療系廃棄物20の滅菌処理に利用された約250 kg/1サイクルの高圧蒸気から凝縮した滅菌処理使用後の水は、排水配管17を経由して水処理設備12に搬送し、水処理設備12でガス化溶融設備1で循環使用する冷却水等と一緒に処理することで、ガス化溶融設備の冷却水等に再利用した。 Here, an embodiment in which a steam sterilization autoclave type sterilization facility 15 is disposed close to the machine side of the gasification and melting facility 1 shown in FIG. explain. The gasification and melting facility 1 can process waste at 9 t / h, and can supply 10 t / h of fuel gas by supplying 6 t / h of oxygen in the high temperature reactor 5. The gas boiler using the fuel gas can generate high-pressure steam of 7 t / h and is used for power generation by the power generation facility 11. Moreover, the water treatment facility of the gasification and melting facility 1 can treat 4 t / h of ring water. In this example, the medical waste 20 is received, and the sterilization equipment 15 uses about 250 kg high-pressure steam per cycle, the sterilization temperature is 135 ° C., and 4 m 3 medical waste (about 1 to 2t) was sterilized in about 1 hour. At that time, the sterilization treatment of the medical waste 20 was performed using a part of the high-pressure steam generated in the gas boiler of the power generation facility 11 before charging the gasification melting facility 1. In addition, the sterilized water condensed from the high-pressure steam of approximately 250 kg / 1 cycle used for sterilization of medical waste 20 is transported to the water treatment facility 12 via the drainage pipe 17, By treating with the cooling water etc. which are circulated and used in the gasification melting equipment 1 in the processing equipment 12, it was reused for the cooling water etc. of the gasification melting equipment.

滅菌処理した医療系廃棄物20中、脱脂綿、包帯、紙オムツ等の高カロリーでかつ低灰分である炭化可能物は、ガス化溶融設備1の高温反応炉5で酸素と反応させる原料の一部として有効利用され、しかも、医療系廃棄物20に含まれる危険な注射針やメス等の低カロリーでかつ高灰分である炭化不可能物は、ガス化溶融設備1の高温反応炉5で1600℃以上の高温で溶融され、高温反応炉5の底部から、スラグとメタルからなる残渣物として合計で1t/h程度回収された。上記の医療系廃棄物の処理により、安全にかつエネルギー効率よく、医療系廃棄物を処理することができた。   Among the sterilized medical waste 20, carbonized materials with high calories and low ash content such as absorbent cotton, bandages, paper diapers, etc. are part of the raw materials that are reacted with oxygen in the high temperature reactor 5 of the gasification melting equipment 1 In addition, low-calorie and high-ash non-carbonized materials such as dangerous needles and scalpels contained in medical waste 20 are 1600 ° C in the high-temperature reactor 5 of the gasification and melting facility 1 It was melted at the above high temperature, and was recovered from the bottom of the high temperature reactor 5 as a residue consisting of slag and metal in total of about 1 t / h. By the treatment of the above medical waste, it was possible to treat the medical waste safely and efficiently.

本発明の実施の形態にかかる医療系廃棄物の処理設備の構成を示す模式図である。It is a schematic diagram which shows the structure of the treatment facility of the medical waste concerning embodiment of this invention. 従来のガス化溶融設備の模式図である。It is a schematic diagram of the conventional gasification melting equipment. 従来の医療系廃棄物の処理フロー図である。It is a processing flowchart of the conventional medical waste.

符号の説明Explanation of symbols

1 ガス化溶融設備
2 廃棄物
3 ピット
3a 廃棄物搬送設備
4 トンネル式加熱炉
5 高温反応炉
6 残渣物
7 急速水冷設備
10 ガス精製設備
11 発電設備
12 水処理設備
15 滅菌処理設備(蒸気滅菌オートクレーブ)
16 蒸気配管
17 排水配管
20 医療系廃棄物
30 一般廃棄物
30A 混合廃棄物
40 病院等の医療機関
50 回収工程
1 Gasification and melting equipment 2 Waste 3 Pit
3a Waste transport equipment 4 Tunnel-type heating furnace 5 High-temperature reactor 6 Residue 7 Rapid water cooling equipment
10 Gas purification equipment
11 Power generation equipment
12 Water treatment facility
15 Sterilization equipment (steam sterilization autoclave)
16 Steam piping
17 Drainage piping
20 Medical waste
30 General waste
30A mixed waste
40 Medical institutions such as hospitals
50 Recovery process

Claims (8)

廃棄物のガス化溶融設備を用いた医療系廃棄物の処理方法であって、前記医療系廃棄物を受け入れて滅菌処理する工程と、該滅菌処理した医療系廃棄物をガス化溶融設備へ装入する前に一旦貯留保持する工程と、該貯留保持した医療系廃棄物を他の廃棄物と混合して前記ガス化溶融設備に装入する工程とを、前記ガス化溶融設備の設置場所に同時に有するようにしたことを特徴とする医療系廃棄物の処理方法。   A method of treating medical waste using a waste gasification and melting facility, the step of receiving and sterilizing the medical waste, and installing the sterilized medical waste into the gasification and melting facility. A step of temporarily storing and holding before entering, and a step of mixing the stored medical waste with other waste and charging it into the gasification and melting equipment at the installation location of the gasification and melting equipment. A method for treating medical waste, characterized in that it has at the same time. 前記ガス化溶融設備に装入する工程において、回収される燃料ガスの発熱量に応じて、医療系廃棄物の装入割合を調整して前記ガス化溶融設備で医療系廃棄物を処理することを特徴とする請求項1に記載の医療系廃棄物の処理方法。  In the step of charging into the gasification and melting equipment, the medical waste is processed in the gasification and melting equipment by adjusting the charging rate of the medical waste according to the calorific value of the recovered fuel gas. The method for treating medical waste according to claim 1. 前記ガス化溶融設備で発生したエネルギーの一部を利用して前記医療系廃棄物の滅菌処理を行うように構成して前記ガス化溶融設備で医療系廃棄物を処理するようにしたことを特徴とする請求項1又は2に記載の医療系廃棄物の処理方法。   The medical waste is sterilized using a part of the energy generated in the gasification and melting equipment, and the medical waste is processed in the gasification and melting equipment. The method for treating medical waste according to claim 1 or 2. 前記医療系廃棄物の滅菌処理を蒸気により行うように構成するとともに、前記蒸気が凝縮して生じた滅菌処理使用後の水を前記ガス化溶融設備の水処理設備で処理するようにしたことを特徴とする請求項1〜3のいずれかに記載の医療系廃棄物の処理方法。   The medical waste is configured to be sterilized by steam, and the water after use of the sterilization generated by condensation of the steam is treated by the water treatment facility of the gasification melting facility. The method for treating medical waste according to any one of claims 1 to 3. 前記医療系廃棄物を受け入れて滅菌処理する工程と、前記ガス化溶融設備に装入する工程とを相互補完的に行って前記ガス化溶融設備で医療系廃棄物を処理することを特徴とする請求項1〜4のいずれかに記載の医療系廃棄物の処理方法。  The medical waste is treated in the gasification and melting equipment by mutually complementing the step of receiving and sterilizing the medical waste and the step of charging into the gasification and melting equipment. The processing method of the medical waste in any one of Claims 1-4. 前記医療系廃棄物中に金属製医療器具を含み、該金属製医療器具の金属分を溶融処理し、メタルとして回収しつつ、前記ガス化溶融設備で医療系廃棄物を処理することを特徴とする請求項1〜5のいずれかに記載の医療系廃棄物の処理方法。   A metal medical instrument is included in the medical waste, the metal waste of the metal medical instrument is melted and recovered as metal, and the medical waste is processed in the gasification melting facility. A method for treating medical waste according to any one of claims 1 to 5. 廃棄物のガス化溶融設備を用いた医療系廃棄物の処理装置であって、前記ガス化溶融設備には、受け入れた医療系廃棄物を滅菌処理する滅菌処理設備と、該滅菌処理設備で滅菌処理した医療系廃棄物を前記滅菌処理設備へ装入する前に一旦貯留保持するピットと、該ピットで貯留保持した医療系廃棄物を他の廃棄物と混合して混合廃棄物として貯留保持するピットと、該混合廃棄物を前記ガス化溶融設備に装入する廃棄物搬送設備と、が近接配置され、前記滅菌処理設備が、前記ガス化溶融設備で発生したエネルギーの一部を利用して前記医療系廃棄物の滅菌処理を行うことが可能なように前記ガス化溶融設備の発電設備と接続されていることを特徴とする医療系廃棄物の処理設備。   A medical waste processing apparatus using a waste gasification and melting equipment, wherein the gasification and melting equipment includes a sterilization equipment for sterilizing received medical waste, and sterilization by the sterilization equipment. Prior to charging the treated medical waste into the sterilization facility, the pit is temporarily stored and held, and the medical waste stored and held in the pit is mixed with other waste and stored as mixed waste. A pit and a waste transport facility for charging the mixed waste into the gasification and melting facility are arranged close to each other, and the sterilization facility uses a part of the energy generated in the gasification and melting facility. A treatment facility for medical waste, wherein the treatment facility is connected to a power generation facility of the gasification and melting facility so that the medical waste can be sterilized. 前記滅菌処理設備が、前記ガス化溶融設備の発電設備で用いる蒸気を発生させるガスボイラと蒸気配管で接続されているとともに、前記ガス化溶融設備の水処理設備と滅菌処理使用後の水を搬送する排水配管で接続されていることを特徴とする請求項7に記載の医療系廃棄物の処理設備。   The sterilization equipment is connected to a gas boiler that generates steam used in the power generation equipment of the gasification and melting equipment and a steam pipe, and transports water after use of the sterilization processing and the water treatment equipment of the gasification and melting equipment. The treatment facility for medical waste according to claim 7, wherein the treatment facility is connected by a drain pipe.
JP2005163578A 2005-06-03 2005-06-03 Method for treating medical waste and facility thereof Pending JP2006336955A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2005163578A JP2006336955A (en) 2005-06-03 2005-06-03 Method for treating medical waste and facility thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2005163578A JP2006336955A (en) 2005-06-03 2005-06-03 Method for treating medical waste and facility thereof

Publications (1)

Publication Number Publication Date
JP2006336955A true JP2006336955A (en) 2006-12-14

Family

ID=37557657

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2005163578A Pending JP2006336955A (en) 2005-06-03 2005-06-03 Method for treating medical waste and facility thereof

Country Status (1)

Country Link
JP (1) JP2006336955A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008266394A (en) * 2007-04-17 2008-11-06 Almighty:Kk Waste plastics treating system
WO2011072136A2 (en) * 2009-12-11 2011-06-16 The Insite Group Re Llc Method and system for the processing of medical and other wastes with integrated waste to energy conversion
CN103090398A (en) * 2013-03-01 2013-05-08 福建省丰泉环保控股有限公司 System and technology for comprehensively treating and utilizing mycelia waste produced in pharmaceutical industry in recycling mode

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008266394A (en) * 2007-04-17 2008-11-06 Almighty:Kk Waste plastics treating system
WO2011072136A2 (en) * 2009-12-11 2011-06-16 The Insite Group Re Llc Method and system for the processing of medical and other wastes with integrated waste to energy conversion
WO2011072136A3 (en) * 2009-12-11 2011-10-20 The Insite Group Re Llc Method and system for the processing of medical and other wastes with integrated waste to energy conversion
CN103090398A (en) * 2013-03-01 2013-05-08 福建省丰泉环保控股有限公司 System and technology for comprehensively treating and utilizing mycelia waste produced in pharmaceutical industry in recycling mode

Similar Documents

Publication Publication Date Title
Messerle et al. Processing of biomedical waste in plasma gasifier
BRPI0607812A2 (en) process for waste treatment and apparatus for carrying out the process
JP2018501080A (en) Infectious waste disposal
JP2006297210A (en) Combined waste treatment facilities
JP2005319373A (en) Method and apparatus for converting sludge into fuel
CN113877940B (en) Medical waste treatment process
JP2006348302A (en) Method and apparatus for converting sludge into fuel
JP2006336955A (en) Method for treating medical waste and facility thereof
JP4378360B2 (en) Power generation method and apparatus using waste
JP2015224795A (en) Generator for fuel gas from organic materials and utilization of heat of same
Messerle et al. Plasma-chemical waste processing: numerical analysis and experiment. Part 1: Medical-biological waste and fuel biomass
JP2001327950A (en) Incineration method and apparatus for solid waste
JP4211118B2 (en) Method and apparatus for producing activated carbon from waste
JP2009102594A (en) Gasification furnace system
JP2003320359A (en) Method and apparatus for pyrolyzing organic waste
JP2005199112A (en) Recycling method for wood
JP2011068824A (en) Carbonization facility for organic water-containing waste
JP4702868B2 (en) Organic waste processing method and processing equipment
JP2009051867A (en) Method for treating medical treatment-based plastic waste or the like and apparatus for treating the same
JP2005052690A (en) Processing system and processing method for effectively utilizing biomass resources
JP3748157B2 (en) Waste treatment system
JPS6322874B2 (en)
US20200368376A1 (en) Method and apparatus for nitrogen filled chamber carbonization of waste material
JP4702869B2 (en) Waste treatment method and treatment equipment
KR100582561B1 (en) A waste carbonizing device

Legal Events

Date Code Title Description
A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A712

Effective date: 20070613