JP2002115820A - Method for waste combustion - Google Patents

Method for waste combustion

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Publication number
JP2002115820A
JP2002115820A JP2000307219A JP2000307219A JP2002115820A JP 2002115820 A JP2002115820 A JP 2002115820A JP 2000307219 A JP2000307219 A JP 2000307219A JP 2000307219 A JP2000307219 A JP 2000307219A JP 2002115820 A JP2002115820 A JP 2002115820A
Authority
JP
Japan
Prior art keywords
water
waste
oil
combustion
fuel
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
JP2000307219A
Other languages
Japanese (ja)
Inventor
Hidetoshi Nakanishi
英敏 中西
Saburo Ishiguro
三郎 石黒
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.)
NAKANISHI GIKEN KK
Original Assignee
NAKANISHI GIKEN KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by NAKANISHI GIKEN KK filed Critical NAKANISHI GIKEN KK
Priority to JP2000307219A priority Critical patent/JP2002115820A/en
Publication of JP2002115820A publication Critical patent/JP2002115820A/en
Pending legal-status Critical Current

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  • Incineration Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To effect perfect decomposition of a benzene ring, which is believed to constitute recombination of dioxin at the time of waste combustion. SOLUTION: Waste is burned by using water-added fuel obtained by mixing oil with water in a ratio 1 to (2-5). In producing the water-added fuel, waste (waste oil, PCB, etc.), is dissolved or suspended in oil, and the obtained water- added fuel is used in waste combustion.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、廃棄物の安全な燃
焼方法に関する。
[0001] The present invention relates to a method for safely burning waste.

【0002】[0002]

【従来の技術】廃棄物の燃焼の際ダイオキシンの発生を
防ぐことが重要である。ケミカルエンジニアリング19
98年4月号によれば通常の燃焼炉では850℃以上の
温度で2秒間以上滞留すれば、ダイオキシンが分解する
が、廃ガスの冷却時にダイオキシンの再生成を防ぐため
に、廃ガスの急冷、洗浄、活性炭吸着などが必要となつ
ている。しかしダイオキシンの規制値は年々厳しくなつ
ており、最近ではミニ高炉の利用、灰の溶融、超臨界水
による酸化分解等が開発されている。しかし炉を高温に
すればダイオキシンの発生は押えられるが、反面NOX
の増加、コスト上昇などが問題となつている。
2. Description of the Related Art It is important to prevent the generation of dioxins when burning waste. Chemical Engineering 19
According to the April 1998 issue, dioxin is decomposed if it stays at a temperature of 850 ° C. or more for 2 seconds or more in a normal combustion furnace, but in order to prevent re-generation of dioxin when cooling the waste gas, quenching of the waste gas, Cleaning and activated carbon adsorption are required. However, the regulation value of dioxin is becoming stricter year by year, and recently, use of mini-blast furnaces, melting of ash, oxidative decomposition with supercritical water, and the like have been developed. However, if the furnace is heated to a high temperature, the generation of dioxin can be suppressed, but NOX
Increasing costs and increasing costs have become problems.

【0003】[0003]

【発明が解決しようとする課題】ダイオキシンは850
℃以上で分解するが、廃ガスを冷却する時再生成するこ
とが問題である。これは廃棄物を燃焼する際ベンゼン環
が燃えにくいため、少しでもベンゼン環が残存すると空
気中の微量な塩素を吸着してダイオキシンが再生成する
といわれる。従って燃焼の際完全にベンゼン環を分解す
れば、冷却時にダイオキシンの再生成もないわけで、ベ
ンゼン環の完全分解燃焼が本発明の課題である。
Dioxin is 850.
Decomposes above ℃, but it is problematic to regenerate when the waste gas is cooled. This is because the benzene ring is difficult to burn when burning waste, and it is said that if a little benzene ring remains, dioxin is regenerated by adsorbing a small amount of chlorine in the air. Therefore, if the benzene ring is completely decomposed during combustion, there is no regeneration of dioxin during cooling, and the subject of the present invention is complete decomposition and combustion of the benzene ring.

【0004】[0004]

【課題を解決するための手段】本発明の手段は下記のと
おりである。 (1)油1:水2〜5の加水燃料を使用して廃棄物を燃
焼させることを特徴とする廃棄物の燃焼方法。 (2)油1:水2〜5の加水燃料を製造する際に油に廃
棄物を溶解又は懸濁させた加水燃料を燃焼させることを
特徴とする廃棄物の燃焼方法。
The means of the present invention are as follows. (1) Oil 1: A waste combustion method characterized in that waste is burned using a water-based fuel of 2 to 5 water. (2) Oil 1: A waste combustion method characterized by burning a water-soluble fuel in which a waste is dissolved or suspended in oil when producing a water-fuel with 2 to 5 water.

【0005】[0005]

【発明の実施の形態】廃棄物を燃焼する場合ベンゼン環
と塩素が存在するとダイオキシン類を生成し易い。最近
では規制が厳しくなり、0.1ng/m3以下も問題にな
り、廃棄物に塩素が含まれなくとも、ベンゼン環が存在
すると空気中の塩素と反応してダイオキシンが生成され
ることも指摘されている。ベンゼン環を分解するには温
度を上げて酸化するだけでは中々分解しない。ダイオキ
シンの分解は少くとも850℃できれば1.100℃以
上の温度に加熱する必要があるが、これはベンゼン環と
塩素の分離であつて、冷却時再結合する可能性があり、
再結合を防ぐには、ベンゼン環を開環・酸化するのが最
も安全な方法である。
BEST MODE FOR CARRYING OUT THE INVENTION In the case of burning waste, the presence of a benzene ring and chlorine tends to generate dioxins. In recent years, regulations have become stricter, and the problem of 0.1 ng / m 3 or less has become a problem. Even if the waste does not contain chlorine, the presence of a benzene ring will react with chlorine in the air to generate dioxin. Have been. In order to decompose the benzene ring, simply raising the temperature and oxidizing does not result in any decomposition. Decomposition of dioxin requires heating to a temperature of at least 1.100 ° C if at least 850 ° C is possible, but this is a separation of benzene ring and chlorine, which may recombine upon cooling.
The safest way to prevent recombination is to open and oxidize the benzene ring.

【0006】石油に5〜30%の水を加えてカーボンの
焼きつきを防ぎ、燃焼効率を上げる方法が従来から行わ
れてきた。しかし1M3当り0.1ng(ナノグラム)以下
という微量のダイオキシンが問題となると、5〜30%
の水の添加では不充分である。本発明は油1に対し2〜
5倍の水を加えた加水燃料を燃焼する方法を活用した発
明である。通常油1に対し50%以上の水を加えると水
を蒸発させる熱量が余分に掛り、温度が上らず次第に消
えるというのが一般的であつた。
Conventionally, a method of adding 5 to 30% of water to petroleum to prevent seizure of carbon and increase combustion efficiency has been used. However, dioxin trace amounts of 1M 3 per 0.1ng (nanograms) The following is a problem, 5-30%
Addition of water is not sufficient. In the present invention, two to two oils are used.
This is an invention utilizing a method of burning a hydrofuel with five times the amount of water. Generally, when 50% or more of water is added to 1 oil, the amount of heat for evaporating the water is extra, and the temperature generally does not rise and gradually disappears.

【0007】しかし発明者等が特願平11−3744
0、特願平11−193032、特願2000−284
840の方法を用い、出口をやゝ狭めた燃焼炉の温度を
別のバーナーで600℃以上に加熱しておき、油1に対
し2〜5倍の水を加えて乳化した加水燃料を噴霧すると
水蒸気爆発による衝撃波のエネルギーが燃焼炉にため込
まれてH2Oは2H+Oに分解し、燃焼炉の外側に油と
共に噴出し燃焼する。この時噴出するガスは油+2H+
O+空気となるが、油はエマルジョンが水蒸気爆発する
際超微細状態となり、分解して一部酸化していると考え
られる。
[0007] However, the inventors have filed Japanese Patent Application No. 11-3744.
0, Japanese Patent Application No. 11-1903032, Japanese Patent Application 2000-284
Using the method of 840, the temperature of the combustion furnace whose outlet is slightly narrowed is heated to 600 ° C. or more by another burner, and water is added to oil 1 to 2 to 5 times and emulsified water spray is sprayed. The energy of the shock wave due to the steam explosion is stored in the combustion furnace, and H 2 O is decomposed into 2H + O, and is ejected and burned with oil outside the combustion furnace. At this time, the gas ejected is oil + 2H +
Although it becomes O + air, the oil is considered to be in an ultrafine state when the emulsion undergoes steam explosion, decomposed and partially oxidized.

【0008】燃焼炉の外側に噴出したこの混合ガスは酸
化して最終的にはCO2とH2Oになるが、表1の分析値
に示す如く、加水燃料では炭素が完全燃焼しCO2とな
り、COがゼロになることが特徴である。(加水燃料は
燃焼性が良い)
[0008] The gas mixture ejected to the outside of the combustion furnace is oxidized and eventually becomes CO 2 and H 2 O. As shown in the analysis values in Table 1, the complete combustion of carbon and the CO 2 The characteristic is that CO becomes zero. (Hydrofuel has good flammability)

【表1】A重油と加水燃料廃ガス比較 [Table 1] Comparison of heavy fuel oil A and hydrofuel waste gas

【0009】本発明はこの油に廃棄物(廃油PCBな
ど)を加えて、2〜5倍の水と共に混合乳化して完全燃
焼させることを特徴としている。600℃〜1.200
℃に加熱された燃焼炉に2〜5倍の水と共に乳化された
廃棄物(廃油PCBなど)を噴霧する。これは従来の燃
料油に5〜30%の水を添加したものと比べると(油を
灯油とし、C1226と仮定してH2O/Cの比率を算出
した。) 従来法(油1:水5〜30%=0.05〜0.3) H2O/C=0.04〜0.24 本発明(油1:水2〜5倍) H2O/C=1.57〜3.94 H2O/Cを比較すると本発明は従来法に比べてH2Oの
量は平均して10倍以上で、C原子に対しH2Oは1.5
〜4倍となる。炭素と水は700℃以上で反応し(水性
ガス反応)C+H2O → CO+H2となることが知られ
ている。
The present invention is characterized in that wastes (such as waste oil PCBs) are added to this oil, mixed and emulsified with 2 to 5 times the amount of water and completely burned. 600 ° C to 1.200
Spray emulsified waste (such as waste oil PCB) with 2 to 5 times water in a combustion furnace heated to ° C. This is compared with a conventional fuel oil in which 5 to 30% of water is added (the oil was used as kerosene and the ratio of H 2 O / C was calculated assuming C 12 H 26 ). 1: water 5~30% = 0.05~0.3) H 2 O / C = 0.04~0.24 present invention (oil 1: 2 to 5 times water) H 2 O / C = 1.57 in ~3.94 H 2 O / If C comparing the present invention is the amount of H 2 O in comparison with the conventional method on average 10 times more, H 2 O whereas C atoms 1.5
Up to 4 times. It is known that carbon and water react at a temperature of 700 ° C. or higher (water gas reaction) to form C + H 2 O → CO + H 2 .

【0010】燃料中に二重結合がある場合、−C=C−
とH2Oが水性ガス類似反応を起し二重結合が破壊され
る。
When there is a double bond in the fuel, -C = C-
And H 2 O cause a water-gas-like reaction to destroy the double bond.

【化1】 炭素二重結合と水の反応 加水燃料中にに廃棄物(廃油やPCBなど)を混入した
場合、その中に含まれるベンゼン環は二重結合3個持つ
ており、その一つにH2Oが反応すればベンゼン環は開
環して、脂肪族に変る。
Embedded image Reaction of carbon double bond with water When waste (waste oil, PCB, etc.) is mixed in the fuel, the benzene ring contained therein has three double bonds, and if one of them reacts with H 2 O, the benzene ring opens. Rings and turns into aliphatic.

【化2】 ベンゼン環と水の反応 Embedded image Reaction of benzene ring with water

【0011】また全部の二重結合にH2Oが作用すれ
ば、アセトアルデヒドに変り酸化し易くなる。加水燃料
の燃焼は油1:水2〜5のエマルジョンを予め600〜
1.200℃の温度に加熱した出口を狭められた燃焼炉
に噴霧する。噴霧された加水燃料中の水は常温から60
0〜1.200℃に急熱されて水蒸気爆発を起す。水蒸
気爆発のエネルギーは衝撃波となつて燃焼炉の壁に衝突
するが、燃焼炉の出口が狭まつているので、この水蒸気
爆発のエネルギーが炉の中に封じ込まれ、発生する爆発
音の反響も働いてガス状のH2Oに水蒸気爆発のエネル
ギーが集まり、H2O →2H+Oに分解する。
When H 2 O acts on all the double bonds, it is converted to acetaldehyde and easily oxidized. Combustion of the hydrofuel is performed by preparing an emulsion of oil 1: water 2 to 5 in advance of 600 to
1. Spray the outlet heated to a temperature of 200 ° C. into a narrowed combustion furnace. The water in the sprayed water is from normal temperature to 60
Rapidly heated to 0 to 1.200 ° C, causing steam explosion. The energy of the steam explosion collides with the wall of the combustion furnace as a shock wave, but since the exit of the combustion furnace is narrow, the energy of this steam explosion is confined in the furnace and the echo of the generated explosion sound is also affected. The steam explosion energy is collected in the gaseous H 2 O by working, and is decomposed into H 2 O → 2H + O.

【0012】分解した2H+Oと油(一部を廃油やPC
Bで置き換えたもの)はガス化し乍ら狭められた出口よ
り噴出し、酸化燃焼する。この時出口を広げると水蒸気
爆発のエネルギーが放散して、H2O → 2H+Oの分
解が不充分となり加水燃料は燃焼しない。出口より噴出
したガスは2H+O+廃油やPCBを含む油の一部酸化
したもの+空気で、燃焼炉の出口の外側で燃焼する。加
水燃料をエネルギー的に見るとH2O → 2H+O →
2Oの分解エネルギーと結合エネルギーの差を熱量と
して取出すという方法である。
Decomposed 2H + O and oil (partly waste oil or PC
B) is ejected from the narrowed outlet while being gasified, and oxidizes and burns. At this time, if the outlet is widened, the energy of the steam explosion will be dissipated, and the decomposition of H 2 O → 2H + O will be insufficient, and the fuel will not burn. The gas ejected from the outlet is 2H + O + waste oil or a partially oxidized oil containing PCB + air, which burns outside the outlet of the combustion furnace. H 2 O → 2H + O →
In this method, the difference between the decomposition energy and the binding energy of H 2 O is extracted as heat.

【0013】熱力学の法則によれば、水の分解エネルギ
ーと結合エネルギーは全く同一で、従ってこのエネルギ
ーの差はゼロということになる。しかし出口を狭められ
た燃焼炉を予め600〜1.200℃に加熱しておき、
その中に加水燃料を噴霧すると、水蒸気爆発のエネルギ
ーが出口を狭められた燃焼炉の中に封じ込まれてH2
の分解を助け、通常では水の分解温度4.000℃以上
必要であるが、この方法を使用すれば水は600〜1.
200℃で分解するので、水の分解エネルギーと結合エ
ネルギーに差が出るわけである。
According to the laws of thermodynamics, the decomposition energy and the binding energy of water are exactly the same, so that the difference between these energies is zero. However, the combustion furnace whose outlet was narrowed was heated to 600 to 1.200 ° C in advance,
When the fuel is sprayed therein, the energy of the steam explosion is trapped in a combustion furnace having a narrowed outlet, and H 2 O
The decomposition temperature of water is usually required to be 4.000 ° C. or higher.
Since it decomposes at 200 ° C., there is a difference between the decomposition energy and the binding energy of water.

【0014】本発明はこの加水燃料の油に廃棄物(廃油
やPCBなど)を混合して燃焼させる方法である。廃棄
物中のベンゼン環は水蒸気爆発のエネルギーを受け乍ら
2O → 2H+O → H2Oの中で反応を受けるわけ
で、通常の水性ガス類似反応以上の反応性を示し、分解
・酸化する。即ち、ベンゼン環は単なる水蒸気反応では
なく、水素原子、酸素原子の他H+、O-、OHラジカル
等が爆発エネルギーを受け乍らプラズマ的反応するわけ
で、ベンゼン環の破壊は急速に進む。
The present invention is a method of mixing waste oil (waste oil or PCB) with the oil of the hydrofuel and burning it. The benzene ring in the waste undergoes a reaction in the form of H 2 O → 2H + O → H 2 O while receiving the energy of steam explosion. . That is, the benzene ring is not just water vapor reaction, other H + hydrogen atom, an oxygen atom, O -, not OH radicals and the like is notwithstanding et plasma reaction undergone explosive energy, destruction of the benzene ring proceeds rapidly.

【0015】[0015]

【実施例】次に本発明を図面について詳細に説明する。
油に溶解する廃棄物(廃油やPCBなど)は油1:水2
〜5の加水燃料製造の際油に混入させる。混入の比率は
通常20〜80%であるが、不燃性の場合は比率は少な
く、可燃性の廃油の場合は100%もあり得る。その油
に界面活性剤と水を加え、エマルジョンを製作する。1
の加水燃料燃焼装置を予め600〜1.200℃に加熱
しておき、廃棄物含有加水燃料を噴霧すると水蒸気爆発
を起し、衝撃波を生じ、出口が狭められているのでその
エネルギーが封じ込まれてH2O → 2H+Oの分解と
共に廃棄物も爆発の余波で微小粒子となり、一部酸化が
進む。
BRIEF DESCRIPTION OF THE DRAWINGS FIG.
Waste dissolved in oil (waste oil, PCB, etc.) is oil 1: water 2
Mixed with oil during the production of the hydrofuel. The mixing ratio is usually 20 to 80%, but the ratio is small in the case of non-flammable and may be 100% in the case of combustible waste oil. A surfactant and water are added to the oil to form an emulsion. 1
Is heated to 600 to 1.200 ° C in advance, and spraying the waste-containing hydrofuel causes a steam explosion, causing a shock wave, and the energy is confined because the outlet is narrowed. With the decomposition of H 2 O → 2H + O, the waste also becomes fine particles in the aftermath of the explosion, and partial oxidation proceeds.

【0016】炉の出口から噴出するガスは2H+O+廃
棄物・油の微小粒子+空気で、それが加水燃料燃焼炎8
となつて回転炉6中で燃焼する。2H+Oは自己燃焼性
のガスなので、空気量は廃棄物・油を充分燃焼させる量
で良く、通常の油燃焼に比べて1/3〜1/5で良い。
この時の回転炉6の温度は700〜900℃で、更に加
熱して反応を完全にするため回転炉9に導入する。回転
炉9は二次加水燃料燃焼装置2のデストリビューター3
で分散した燃料炎11で廃ガスと充分に攪拌し、温度を
1.000〜1.200℃とし反応を進める。この加水燃
料は油1:水2〜5であるが、二次の加水燃料には廃棄
物を入れずに回転炉9の加熱を行う。この時回転炉6で
充分燃焼されなかつた廃棄物は更に2H+O → H2
の中で燃焼分解する。特に燃焼しにくいベンゼン環も回
転炉6、9で圧倒的多量のH2Oの中で水性ガス類似反
応が進み、分解酸化する。
The gas ejected from the outlet of the furnace is 2H + O + fine particles of waste and oil + air, which is a combustion fuel combustion flame 8
Then, it burns in the rotary furnace 6. Since 2H + O is a self-combustible gas, the amount of air may be sufficient to burn waste and oil sufficiently, and may be 1/3 to 1/5 of that of normal oil combustion.
At this time, the temperature of the rotary furnace 6 is 700 to 900 ° C., and the mixture is further introduced into the rotary furnace 9 to complete the reaction. The rotary furnace 9 is a distributor 3 of the secondary water-fuel combustion device 2.
The mixture is sufficiently stirred with the waste gas with the fuel flame 11 dispersed in the above, and the temperature is set to 1.000 to 1.200 ° C. to proceed the reaction. This hydrofuel is oil 1: water 2 to 5, but the rotary furnace 9 is heated without putting waste into the secondary hydrofuel. At this time, the waste that has not been sufficiently burned in the rotary furnace 6 further contains 2H + O → H 2 O
Decomposes in combustion. In particular, a benzene ring which is not easily burned is decomposed and oxidized in the rotary furnaces 6 and 9 in a water gas-like reaction in an overwhelmingly large amount of H 2 O.

【0017】特にこの場合単なる水蒸気でなく、H2
→ 2H+O → H2Oの工程中の水で、活性化された形
で反応するので、ベンゼン環の分解が進む。この時灰化
する固体は水封した灰の排出口14より排出する。廃ガ
スは更に三次加水燃料燃焼装置2aによりセラミック充
填層16中で混合酸化分解し、ダイオキシンゼロ、残留
ベンゼンゼロを達成する。廃ガス17は熱量回収、水洗
等の工程を経て放出する。
In this case, not only water vapor but also H 2 O
The reaction proceeds in an activated form with water in the process of → 2H + O → H 2 O, so that the decomposition of the benzene ring proceeds. At this time, the solidified ash is discharged from the water-sealed ash discharge port 14. The waste gas is further mixed and oxidized and decomposed in the ceramic packed bed 16 by the tertiary water-fuel combustion device 2a to achieve zero dioxin and zero residual benzene. The waste gas 17 is released through processes such as heat recovery and water washing.

【0018】固形の廃棄物の場合は加水燃料燃焼装置1
で予め回転炉6を加熱しておき、粉砕した廃棄物を投入
口4より連続投入する。回転炉6で95〜99%のダイ
オキシン類は除去されるが、更に回転炉9で二次加水燃
料燃焼装置2、デイストリビューター3により分散した
燃焼炎11により1.000〜1.200℃に加熱し、ダ
イオキシンを完全に分解する。ダイオキシンを除去した
灰は水封した灰の排出口14より外部に搬出する。ダイ
オキシン汚染土を処理した場合ダイオキシン含有量は1
/3.000〜1/10.000となる。また処理しにく
い廃水を加水燃料の水として用いて、その加水燃料を燃
焼させれば廃水処理と熱量が同時に得られ、シアン廃
水、研磨廃水、プリント基盤製造廃水などが簡単に処理
できる。またこの装置の冷却洗浄水も加水燃料の水とし
て使用すればクローズドシステムとなる。
In the case of solid waste, the fuel-burning combustion device 1
, The rotary furnace 6 is preliminarily heated, and the crushed waste is continuously charged from the charging port 4. Although 95 to 99% of dioxins are removed in the rotary furnace 6, the dioxin is further cooled to 1,000 to 1.200 ° C. in the rotary furnace 9 by the secondary flame fuel burner 2 and the combustion flame 11 dispersed by the distributor 3. Heat to completely decompose dioxin. The ash from which dioxin has been removed is carried out through a water-sealed ash outlet 14. Dioxin content is 1 when dioxin contaminated soil is treated
/ 3,000-1 / 10,000. Further, if waste water which is difficult to treat is used as water for adding fuel and the fuel is burned, waste water treatment and calorific value can be obtained at the same time, and cyan waste water, polishing waste water, print substrate manufacturing waste water and the like can be easily treated. Also, if the cooling and washing water of this apparatus is also used as water for the hydrofuel, a closed system is obtained.

【0019】[0019]

【発明の効果】本発明は公害の元となつた観のダイオキ
シン、PCBを効率良く除去する方法に関する発明であ
る。従来ダイオキシン、PCBはミニ高炉、灰溶解炉な
ど超高温で分解する方法や超臨界水による方法等設備費
も掛り、高温の場合はNOXなど別の公害も問題になつ
ている。本発明においては加水燃料を使用するので油の
使用量が1/2〜1/3と少なく、また空気の吹込み量
も油が少ないのでやはり1/2〜1/3になり、N2
少ないためNOXの量も減少する。また本発明の方法は
2Oを使用して燃焼させるので、従来熱では分解しに
くかつたベンゼン環も簡単に分解するので冷却の際ダイ
オキシンの再生成という危険もない。
Industrial Applicability The present invention relates to a method for efficiently removing dioxins and PCBs which has caused pollution. Conventionally, dioxins and PCBs require equipment costs such as a method of decomposing at an extremely high temperature such as a mini blast furnace and an ash melting furnace, and a method of using supercritical water. In the case of a high temperature, another pollution such as NOX is also a problem. Least amount of oil 1 / 2-1 / 3 because it uses hydro fuel in the present invention, also blowing amount of air also becomes still 1 / 2-1 / 3 the oil is small, N 2 is Since it is small, the amount of NOX also decreases. Further, since the method of the present invention uses H 2 O for combustion, the benzene ring which has been hardly decomposed by conventional heat and easily decomposes does not have the danger of regenerating dioxin during cooling.

【0020】しかもこの方法は大型炉にも適用できる
が、中、小型炉に向いており、既存の炉に加水燃料燃焼
装置を設置することも可能で、国家的に見ても非常に経
済的な発明である。次に本発明の利点を列挙すると。 (1)ダイオキシン、PCBを完全に分離燃焼できる。 (2)油使用量1/2〜1/3となり省資源型である。 (3)従来分解しにくかつたベンゼン環を分解燃焼す
る。 (4)NOX、SOX、CO2夫々1/2〜1/3。 (5)既設炉の改造も可能である。 (6)汚染土壌の処理が連続的にできる。
Although this method can be applied to large furnaces, it is suitable for medium and small furnaces, and it is possible to install a water-fuel combustion apparatus in an existing furnace, which is very economical even from the national viewpoint. Invention. Next, the advantages of the present invention will be listed. (1) Dioxin and PCB can be completely separated and burned. (2) The amount of oil used is 2〜 to 1 /, which is a resource saving type. (3) Decompose and burn benzene rings that have been difficult to decompose. (4) NOX, SOX, CO 2 respectively 1 / 2-1 / 3. (5) Existing furnaces can be modified. (6) Contaminated soil can be treated continuously.

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

【図1】 本発明に係る廃棄物の燃焼方法の実施状態
を示す説明図
FIG. 1 is an explanatory view showing an embodiment of a waste combustion method according to the present invention.

【符号の説明】[Explanation of symbols]

1 加水燃料燃焼装置 2 二次加水燃料燃焼装置 2a 三次加水燃料燃焼装置 3 ディストリビューター 3a ディストリビューター 4 廃棄物の投入口 5 廃棄物 6 回転炉 7 耐火材 8 加水燃料燃焼炎 9 回転炉 10 耐火材 11 燃焼炎 12 灰 13 水封用水 14 灰の排出口 15 燃焼炎 16 セラミック充填層 17 廃棄ガス、熱回収、水洗工程への出口 REFERENCE SIGNS LIST 1 fueled fuel combustion device 2 secondary fueled fuel combustion device 2a tertiary fueled fuel combustion device 3 distributor 3a distributor 4 waste input port 5 waste 6 rotary furnace 7 refractory material 8 hydrofuel combustion flame 9 rotary furnace 10 refractory material Reference Signs List 11 combustion flame 12 ash 13 water for sealing water 14 ash outlet 15 combustion flame 16 ceramic packed bed 17 waste gas, heat recovery, exit to washing process

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F23G 7/04 603 F23G 7/04 603A ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F23G 7/04 603 F23G 7/04 603A

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 油1:水2〜5の加水燃料を使用して廃
棄物を燃焼させることを特徴とする廃棄物の燃焼方法。
1. A method for burning waste, comprising burning waste using oil-to-water fuel of 2 to 5 oils.
【請求項2】 油1:水2〜5の加水燃料を製造する際
に油に廃棄物を溶解又は懸濁させた加水燃料を燃焼させ
ることを特徴とする廃棄物の燃焼方法。
2. A method for burning waste, characterized in that when producing a water-to-fuel fuel of oil 1: water 2 to 5, water-soluble fuel in which waste is dissolved or suspended in oil is burned.
【請求項3】 油1:水2〜5の加水燃料を製造する際
に水の代りに廃水を使用した加水燃料を燃焼させること
を特徴とする廃棄物の燃焼方法。
3. A method for burning waste, characterized in that a hydrofuel using wastewater instead of water is burned when producing a hydrofuel of oil 1 to water 2-5.
【請求項4】 必要に応じて二次的、三次的に油1:水
2〜5の加水燃料で追加燃焼することを特徴とする請求
項1、2、3記載の廃棄物の燃焼方法。
4. The method for burning waste according to claim 1, wherein the fuel is additionally combusted secondary or tertiary as needed with an oil 1: water 2 to 5 hydrofuel.
JP2000307219A 2000-10-06 2000-10-06 Method for waste combustion Pending JP2002115820A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000307219A JP2002115820A (en) 2000-10-06 2000-10-06 Method for waste combustion

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000307219A JP2002115820A (en) 2000-10-06 2000-10-06 Method for waste combustion

Publications (1)

Publication Number Publication Date
JP2002115820A true JP2002115820A (en) 2002-04-19

Family

ID=18787766

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000307219A Pending JP2002115820A (en) 2000-10-06 2000-10-06 Method for waste combustion

Country Status (1)

Country Link
JP (1) JP2002115820A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007032999A (en) * 2005-07-29 2007-02-08 Kuniya Hayashi Incineration system
JPWO2010073710A1 (en) * 2008-12-27 2012-06-14 株式会社ブイエスディー Gasification combustion equipment
CN111288459A (en) * 2020-04-15 2020-06-16 李镐玉 Smokeless incineration device for solid waste combustion

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007032999A (en) * 2005-07-29 2007-02-08 Kuniya Hayashi Incineration system
JPWO2010073710A1 (en) * 2008-12-27 2012-06-14 株式会社ブイエスディー Gasification combustion equipment
CN111288459A (en) * 2020-04-15 2020-06-16 李镐玉 Smokeless incineration device for solid waste combustion

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