JPH04283309A - Method for incinerating waste liquid containing nitrogen compound - Google Patents
Method for incinerating waste liquid containing nitrogen compoundInfo
- Publication number
- JPH04283309A JPH04283309A JP7238591A JP7238591A JPH04283309A JP H04283309 A JPH04283309 A JP H04283309A JP 7238591 A JP7238591 A JP 7238591A JP 7238591 A JP7238591 A JP 7238591A JP H04283309 A JPH04283309 A JP H04283309A
- Authority
- JP
- Japan
- Prior art keywords
- waste liquid
- furnace
- incinerator
- gas
- inlet
- 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
Links
- 239000007788 liquid Substances 0.000 title claims abstract description 45
- 239000002699 waste material Substances 0.000 title claims abstract description 32
- 238000000034 method Methods 0.000 title claims abstract description 16
- 229910017464 nitrogen compound Inorganic materials 0.000 title claims description 11
- 150000002830 nitrogen compounds Chemical class 0.000 title claims description 11
- 238000002485 combustion reaction Methods 0.000 claims abstract description 9
- 239000000446 fuel Substances 0.000 claims abstract description 9
- 150000002897 organic nitrogen compounds Chemical class 0.000 claims abstract description 7
- 239000007789 gas Substances 0.000 abstract description 27
- 239000007921 spray Substances 0.000 abstract description 8
- 238000000354 decomposition reaction Methods 0.000 abstract description 2
- 230000007423 decrease Effects 0.000 abstract description 2
- 238000005507 spraying Methods 0.000 abstract description 2
- 238000009834 vaporization Methods 0.000 abstract description 2
- 230000008016 vaporization Effects 0.000 abstract description 2
- 238000002309 gasification Methods 0.000 abstract 1
- 239000002912 waste gas Substances 0.000 abstract 1
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000002918 waste heat Substances 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- -1 nitrogen-containing compound Chemical class 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は有機質の窒素化合物を含
む廃液を、発生する窒素酸化物の量を抑制して焼却する
ことができる焼却方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for incinerating waste liquid containing organic nitrogen compounds while suppressing the amount of nitrogen oxides generated.
【0002】0002
【従来の技術】従来、有機質の廃液は焼却して無害なC
O2,H2O等にして排出し、公害の発生を防止してい
るが、窒素化合物を含む廃液を焼却すると窒素酸化物N
Ox(NO,NO2,NO3)が発生し、排出ガス中の
NOx濃度が固定発生源の規定濃度である250〜45
0ppmを越えるため、焼却炉のあとにさらに脱硝装置
を設けてNOxの含有量を低下させ、公害防止法の規定
濃度以下の濃度として大気放出している。[Prior Art] Conventionally, organic waste liquid was incinerated to remove harmless carbon dioxide.
It is discharged as O2, H2O, etc. to prevent pollution, but when waste liquid containing nitrogen compounds is incinerated, nitrogen oxides (N) are released.
Ox (NO, NO2, NO3) is generated, and the NOx concentration in the exhaust gas is 250 to 45, which is the specified concentration for fixed sources.
In order to exceed 0 ppm, a denitration device is installed after the incinerator to reduce the NOx content, and the NOx content is released into the atmosphere below the concentration stipulated in the Pollution Control Law.
【0003】0003
【発明が解決しようとする課題】しかしながら、脱硝装
置は、大量のガス中のNOxを触媒に通して減少させる
ため、設備費が高く、また使用していると経時的に触媒
の活性が低下するので定期的な交換が必要となり、運転
費も嵩み、これが設置されたプラントの製品コストが、
高くなる不都合があった。[Problems to be Solved by the Invention] However, since denitrification equipment reduces NOx in a large amount of gas by passing it through a catalyst, the equipment cost is high, and the activity of the catalyst decreases over time when used. Therefore, regular replacement is required, which increases operating costs, and the product cost of the plant where this is installed.
There was an inconvenience that it was expensive.
【0004】本発明者らは、上記の問題を解決すべく鋭
意検討した結果、化合物中のNが酸素と反応してNOx
となる場合、焼却される窒素含有化合物の状態によって
、(a) 固体又は液体状の窒素含有化合物中のNと
O2との反応によってNOxを生成する場合、(b)
ガス状の窒素化合物中のNとO2との反応によってN
Oxを生成する場合、の2通りがあり、化合物中のNが
NOxに変換する割合は、(b)が(a)に比して格段
に小さいことが知られており、これが利用できると考え
た。[0004] As a result of intensive study to solve the above problem, the present inventors found that N in the compound reacts with oxygen and NOx
In this case, depending on the state of the nitrogen-containing compound to be incinerated, (a) if NOx is produced by the reaction of N in the solid or liquid nitrogen-containing compound with O2, (b)
N by the reaction of N in gaseous nitrogen compounds with O2
When generating Ox, there are two ways. It is known that the rate at which N in the compound is converted to NOx is much smaller in (b) than in (a), and we believe that this can be used. Ta.
【0005】本発明は上記の考えに基ずいてなされたも
ので、焼却炉のみによって、焼却炉排出ガス中のNOx
濃度を少なくすることができる焼却方法を提供すること
を目的とする。The present invention has been made based on the above idea, and uses only the incinerator to reduce NOx in the incinerator exhaust gas.
The purpose is to provide an incineration method that can reduce the concentration.
【0006】本発明に係る窒素化合物を含む廃液の焼却
法においては、有機質の窒素化合物を竪型筒状焼却炉の
頂部から噴霧供給し、焼却炉の高さ方向中間に設けられ
たバーナに燃料および空気を導入して焼却する。In the method of incinerating waste liquid containing nitrogen compounds according to the present invention, organic nitrogen compounds are sprayed and supplied from the top of a vertical cylindrical incinerator, and fuel is supplied to a burner installed in the middle of the incinerator in the height direction. and incinerate by introducing air.
【0007】或いは、廃液を予熱し、発生した蒸気を竪
型筒状の焼却炉の上部に導入するとともに、濃縮液を焼
却炉の頂部より噴霧供給し、焼却炉の高さ方向中間部に
設けられたバーナに燃料および空気を導入して、上記導
入されたガスおよび濃縮液を燃焼することを問題解決の
手段とした。Alternatively, the waste liquid is preheated, the generated steam is introduced into the upper part of the vertical cylindrical incinerator, and the concentrated liquid is sprayed and supplied from the top of the incinerator, and the incinerator is installed in the middle part of the incinerator in the height direction. The solution to the problem was to introduce fuel and air into the burner and burn the introduced gas and concentrate.
【0008】[0008]
【作用】本発明の方法は、上記の構成となっているので
、焼却炉下部の燃焼によって、上部も加熱され、噴霧導
入された液は、分解或いは気化によりガス化され、これ
が下部において燃焼焔と混合して焼却される。このよう
にガス化された窒素化合物が焼却されるので排ガス中の
NOx発生量が抑制される。[Operation] Since the method of the present invention has the above-mentioned structure, the upper part is also heated by combustion in the lower part of the incinerator, and the sprayed liquid is gasified by decomposition or vaporization, and this is ignited by the combustion flame in the lower part. It is mixed with and incinerated. Since the gasified nitrogen compounds are incinerated in this way, the amount of NOx generated in the exhaust gas is suppressed.
【0009】[0009]
【実施例】図1は本発明の焼却方法において使用される
竪型焼却炉(以下炉という)1の一例を示すもので、外
側は鉄板によって形成され、内面には耐火物が張られた
円筒状となっている。この炉1上端部はコーン状に形成
され、頂部には廃液を噴霧供給する導入口2が設けられ
ている。この導入口の周囲には、必要に応じて小量の空
気を導入し、噴霧供給された液の一部を燃焼させ炉上部
3の温度を高める上空気導入口5が設けられている。こ
の炉1の高さ方向中間より上の炉1の上部3と下部4の
境界近傍には下空気導入口6a、および燃料導入口6b
を有するバーナ6が火焔を炉1の内壁に対して接線方向
に噴射するように設けられている。また、炉1の下端部
には、燃焼した排出ガスの導出口7が設けられている。
さらに、廃液を加熱(予熱)して蒸気が発生する場合、
この発生した蒸気を分離して炉1の上部に炉内面に対し
て接線方向に吹込むガス導入管8が設けられている。[Example] Fig. 1 shows an example of a vertical incinerator (hereinafter referred to as a furnace) 1 used in the incineration method of the present invention. The situation is as follows. The upper end of this furnace 1 is formed into a cone shape, and an inlet 2 for spraying waste liquid is provided at the top. An upper air inlet 5 is provided around this inlet to introduce a small amount of air as necessary to burn part of the sprayed liquid and raise the temperature of the upper part 3 of the furnace. Near the boundary between the upper part 3 and lower part 4 of the furnace 1 above the middle in the height direction of the furnace 1, there is a lower air inlet 6a and a fuel inlet 6b.
A burner 6 having a burner 6 is provided to emit a flame tangentially to the inner wall of the furnace 1. Further, at the lower end of the furnace 1, an outlet port 7 for the burned exhaust gas is provided. Furthermore, if steam is generated by heating (preheating) waste liquid,
A gas introduction pipe 8 is provided in the upper part of the furnace 1 to separate the generated steam and inject it tangentially to the inner surface of the furnace.
【0010】上記炉1を用いて廃液を焼却するには、先
ず廃液を加熱する。その際蒸気を発生しその量が多い場
合には、これを噴霧導入口2から導入すると、スムース
に導入することが出来ないので蒸気と液とを分離し、蒸
気をガス導入管8より導入する。当然のことだから廃液
を予熱しても、蒸気を発生しないか、極めて少ない場合
にはガス導入管8は必要ない。[0010] In order to incinerate waste liquid using the furnace 1, the waste liquid is first heated. At this time, if steam is generated and its amount is large, it cannot be introduced smoothly if it is introduced from the spray inlet 2, so the steam and liquid are separated and the steam is introduced from the gas introduction pipe 8. . Naturally, even if the waste liquid is preheated, the gas introduction pipe 8 is not necessary if no steam is generated or the amount of steam is extremely small.
【0011】上記炉1の上部3は、炉1の下部4におけ
る燃焼によって、下部4が1000℃以上となっている
ので、主としてその輻射によって850℃以上に保持さ
れる。上記噴霧導入口2及び8から導入された液は高温
に保持されている上部3において、分解或いは蒸発され
、殆んどがガス化される。このガス化された廃液は、下
部4において燃焼焔と混合されるとともに焼却される。
この焼却によって発生した排ガスは、廃液がガス化され
て、しかる後焼却されるので発生するNOx量は少なく
、脱硝装置を使用することなく排ガス中のNOx含有量
を規定濃度以下とすることが出来る。[0011] The upper part 3 of the furnace 1 is maintained at a temperature of 850°C or higher mainly by radiation, since the lower part 4 is at 1000°C or higher due to combustion in the lower part 4 of the furnace 1. The liquid introduced from the spray inlets 2 and 8 is decomposed or evaporated in the upper part 3 kept at a high temperature, and most of it is gasified. This gasified waste liquid is mixed with the combustion flame in the lower part 4 and is incinerated. In the exhaust gas generated by this incineration, the waste liquid is gasified and then incinerated, so the amount of NOx generated is small, and the NOx content in the exhaust gas can be reduced to below the specified concentration without using a denitrification device. .
【0012】上記方法において炉1の上部3を850℃
以上に保持することは、噴霧導入された廃液をガス化す
るために重要で、下部4の濃度を1000℃以上に保持
すれば、上部3における850℃以上の条件は保持され
る。しかし上部3が850℃以下になりそうな場合には
、上空気導入口5より小量の空気を導入すれば噴霧され
た液の一部が燃焼し、上部3内の温度を高くすることが
できる。In the above method, the upper part 3 of the furnace 1 is heated to 850°C.
Maintaining the concentration above this level is important for gasifying the sprayed waste liquid, and if the concentration in the lower part 4 is maintained at 1000°C or higher, the condition of 850°C or higher in the upper part 3 is maintained. However, if the temperature in the upper part 3 is about to drop below 850 degrees Celsius, if a small amount of air is introduced through the upper air inlet 5, a part of the sprayed liquid will burn and the temperature in the upper part 3 can be raised. can.
【0013】なお、上記炉において使用される上下の空
気導入口5および6aから導入される空気量は、廃液お
よび燃料の燃焼に必要な理論空気量の1.3倍程度で、
上空気導入口5から必要に応じて導入される空気量は、
廃液の燃焼に必要な理論空気量の30%以下が望ましい
。すなわち炉上部3での燃焼は極力少なくする。The amount of air introduced from the upper and lower air inlet ports 5 and 6a used in the above furnace is about 1.3 times the theoretical amount of air required for combustion of waste liquid and fuel.
The amount of air introduced from the upper air inlet 5 as needed is:
It is desirable that the amount of air be 30% or less of the theoretical air amount required for combustion of waste liquid. That is, combustion in the upper part 3 of the furnace is minimized.
【0014】図2は、本発明の方法を実施するシステム
の一例を示すもので、図1と同一部分には同一符号を付
してその説明を簡略化する。図において11は、濃縮器
で、濃縮器で発生した蒸気は、炉1のガス導入管8から
導入される。また濃縮液は、ポンプ12によって噴霧導
入口2に送られ、炉1に噴霧供給される。炉1の排ガス
導出口7から排出される高温ガスは廃熱ボイラ13によ
って、水蒸気を発生するとともに降温され排風機14を
介して、排気筒15より大気放出される。上記廃熱ボイ
ラ13で発生した水蒸気は、濃縮器11の熱源として使
用され、ドレインとして系外に放出される。FIG. 2 shows an example of a system for implementing the method of the present invention, and the same parts as in FIG. 1 are given the same reference numerals to simplify the explanation. In the figure, reference numeral 11 denotes a concentrator, and the steam generated in the condenser is introduced from the gas introduction pipe 8 of the furnace 1. Further, the concentrated liquid is sent to the spray inlet 2 by the pump 12 and is supplied to the furnace 1 as a spray. High-temperature gas discharged from the exhaust gas outlet 7 of the furnace 1 generates water vapor and its temperature is lowered by the waste heat boiler 13, and is discharged into the atmosphere from the exhaust stack 15 via the exhaust fan 14. The steam generated in the waste heat boiler 13 is used as a heat source for the condenser 11 and is discharged outside the system as a drain.
【0015】次に実施例、比較例を示して本発明を具体
的に説明する。Next, the present invention will be specifically explained with reference to Examples and Comparative Examples.
【0016】実施例1
図1の炉を用い有機質の窒素化合物を含有する液を80
℃に予熱し、噴霧導入口より供給した。またバーナ6か
ら重油を燃料とし、理論空気量の1.3倍の空気を導入
して焼却した。その結果炉の下部4は1000℃、上部
3は850℃に保持され、排ガス導出口7より排出され
るガスは、1000℃において2600m3/hr、ガ
ス中のNOx濃度は75ppmであった(但しO2 1
2%換算)。Example 1 Using the furnace shown in FIG. 1, a liquid containing an organic nitrogen compound was heated at 80%
It was preheated to ℃ and supplied from the spray inlet. In addition, heavy oil was used as fuel from burner 6, and air in an amount 1.3 times the theoretical air amount was introduced for incineration. As a result, the lower part 4 of the furnace was maintained at 1000°C and the upper part 3 at 850°C, and the gas discharged from the exhaust gas outlet 7 was 2600 m3/hr at 1000°C, and the NOx concentration in the gas was 75 ppm (however, O2 1
2% conversion).
【0017】比較例1
通常の焼却炉を用いた以外は実施例1と同じにした。炉
内温度は1000〜1100℃に保持され、廃液は焼却
されたが排出されるガス中のNOx濃度は750〜11
00ppmであった。Comparative Example 1 The procedure was the same as in Example 1 except that a normal incinerator was used. The temperature inside the furnace was maintained at 1000-1100℃, and the waste liquid was incinerated, but the NOx concentration in the discharged gas was 750-1100℃.
It was 00 ppm.
【0018】[0018]
【発明の効果】以上説明したように、本発明の方法によ
って窒素化合物を焼却すると、炉上部においてガス化さ
れ、これがバーナの火焔と混合して燃焼するので、NO
xの生成が抑制され、排ガス中のNOxは規定濃度以下
となるために脱硝装置の設量を必要としたものが、焼却
炉からの排ガスを直接大気に放出することが可能となり
、その工業的利益は極めて大きい。Effects of the Invention As explained above, when nitrogen compounds are incinerated by the method of the present invention, they are gasified in the upper part of the furnace and mixed with the flame of the burner and combusted.
The production of NOx in the exhaust gas is suppressed and NOx in the exhaust gas is below the specified concentration, which previously required the installation of a denitrification device. The profits are extremely large.
【図1】本発明に使用する焼却炉の一例を示す説明図で
ある。FIG. 1 is an explanatory diagram showing an example of an incinerator used in the present invention.
【図2】図1の焼却炉を用いた廃液焼却システムの一例
を示す図である。FIG. 2 is a diagram showing an example of a waste liquid incineration system using the incinerator of FIG. 1.
1 焼却炉(炉) 2 噴霧導入口 3 炉上部 4 炉下部 5 上空気導入口 6 バーナ 6a 下空気導入口 6b 燃料導入口 7 排ガス導出口 8 ガス導入管 11 濃縮器 12 ポンプ 13 廃熱ボイラ 14 排風機 15 排気筒 1 Incinerator (furnace) 2 Spray inlet 3 Upper part of the furnace 4 Lower part of the furnace 5 Upper air inlet 6 Burner 6a Lower air inlet 6b Fuel inlet 7 Exhaust gas outlet 8 Gas introduction pipe 11 Concentrator 12 Pump 13 Waste heat boiler 14 Exhaust fan 15 Exhaust stack
Claims (5)
、竪型筒状焼却炉の頂部から噴霧供給し、焼却炉の高さ
方向中間に設けられたバーナに燃料および空気を導入し
て、燃焼させることを特徴とする窒素化合物を含む廃液
の焼却方法。Claim 1: A waste liquid containing organic nitrogen compounds is sprayed and supplied from the top of a vertical cylindrical incinerator, and fuel and air are introduced into a burner installed in the middle of the incinerator in the height direction to perform combustion. A method for incinerating waste liquid containing nitrogen compounds.
予熱して焼却炉に供給する請求項1記載の窒素化合物を
含む廃液の焼却方法。2. The method of incinerating a waste liquid containing a nitrogen compound according to claim 1, wherein the waste liquid containing an organic nitrogen compound is preheated and then supplied to an incinerator.
予熱し、発生した蒸気を竪型筒状焼却炉の上部に導入す
るとともに、濃縮液を焼却炉の頂部から噴霧供給し、こ
れらを焼却炉の高さ方向中間部に設けられたバーナに燃
料および空気を導入して、燃焼させることを特徴とする
窒素化合物を含む廃液の焼却方法。[Claim 3] The waste liquid containing organic nitrogen compounds is preheated, the generated steam is introduced into the upper part of the vertical cylindrical incinerator, and the concentrated liquid is sprayed and supplied from the top of the incinerator. A method for incinerating waste liquid containing nitrogen compounds, characterized by introducing fuel and air into a burner installed in the middle part in the height direction and burning the waste liquid.
際し、空気を導入してその一部を燃焼させる請求項1又
は3記載の窒素化合物を含む廃液の焼却方法。4. The method of incinerating a waste liquid containing nitrogen compounds according to claim 1 or 3, wherein air is introduced and a part of the waste liquid is combusted when the waste liquid is sprayed and supplied from the top of the incinerator.
が1000℃以上、上の部分が850℃以上に保持され
る請求項1,2,3又は4記載の窒素化合物を含む廃液
の焼却方法。5. The waste liquid containing nitrogen compounds according to claim 1, 2, 3 or 4, wherein the lower part of the incinerator in the height direction is kept at 1000°C or higher, and the upper part is kept at 850°C or higher. Incineration method.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7238591A JPH04283309A (en) | 1991-03-12 | 1991-03-12 | Method for incinerating waste liquid containing nitrogen compound |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7238591A JPH04283309A (en) | 1991-03-12 | 1991-03-12 | Method for incinerating waste liquid containing nitrogen compound |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04283309A true JPH04283309A (en) | 1992-10-08 |
Family
ID=13487766
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP7238591A Pending JPH04283309A (en) | 1991-03-12 | 1991-03-12 | Method for incinerating waste liquid containing nitrogen compound |
Country Status (1)
Country | Link |
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JP (1) | JPH04283309A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6237512B1 (en) | 1998-02-03 | 2001-05-29 | Kiyoshi Nakato | Waste liquid incinerator and method of incinerating waste liquid |
WO2011083877A1 (en) * | 2010-01-07 | 2011-07-14 | 株式会社アイ・ビー・エス | Method and device for high-temperature combustion using fuel and aqueous solution of organic compound |
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JPS5436075A (en) * | 1977-08-26 | 1979-03-16 | Asahi Chem Ind Co Ltd | Method of treating waste water by way of combustion |
JPS5539725A (en) * | 1978-09-13 | 1980-03-19 | Meiji Seika Kaisha Ltd | Preparation of mayonnaise-like seasoning |
JPS5687716A (en) * | 1979-12-17 | 1981-07-16 | Kubota Ltd | Waste water treating method |
-
1991
- 1991-03-12 JP JP7238591A patent/JPH04283309A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5436075A (en) * | 1977-08-26 | 1979-03-16 | Asahi Chem Ind Co Ltd | Method of treating waste water by way of combustion |
JPS5539725A (en) * | 1978-09-13 | 1980-03-19 | Meiji Seika Kaisha Ltd | Preparation of mayonnaise-like seasoning |
JPS5687716A (en) * | 1979-12-17 | 1981-07-16 | Kubota Ltd | Waste water treating method |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6237512B1 (en) | 1998-02-03 | 2001-05-29 | Kiyoshi Nakato | Waste liquid incinerator and method of incinerating waste liquid |
WO2011083877A1 (en) * | 2010-01-07 | 2011-07-14 | 株式会社アイ・ビー・エス | Method and device for high-temperature combustion using fuel and aqueous solution of organic compound |
JPWO2011083877A1 (en) * | 2010-01-07 | 2013-05-16 | 石黒 三郎 | High temperature combustion method and apparatus using fuel and organic compound aqueous solution |
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