JPH0783425A - Waste oil burner - Google Patents
Waste oil burnerInfo
- Publication number
- JPH0783425A JPH0783425A JP22906793A JP22906793A JPH0783425A JP H0783425 A JPH0783425 A JP H0783425A JP 22906793 A JP22906793 A JP 22906793A JP 22906793 A JP22906793 A JP 22906793A JP H0783425 A JPH0783425 A JP H0783425A
- Authority
- JP
- Japan
- Prior art keywords
- waste oil
- combustion
- nozzle
- pcb
- high heat
- 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.)
- Granted
Links
Abstract
Description
【0001】[0001]
【産業上の利用分野】この発明は、地球環境を破壊する
ものとして各種電気器具などに使用されて来たPCBな
どの公害物質を有効に燃焼させて地球環境の汚染を防止
するようにした燃焼装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention effectively burns pollutants such as PCB, which have been used in various electric appliances for destroying the global environment, to prevent pollution of the global environment. Regarding the device.
【0002】[0002]
【従来の技術】従来、この種のPCBなどの汚染物質を
燃焼処理する装置としては、我が国にあっては燃焼温度
1,150℃、滞溜時間2秒、過剰酸素3%でテストを
行い分解効率が99.9999%すなわち、6−ナイン
が確認されることが装置実施のための必要最低限の条件
であった。2. Description of the Related Art Conventionally, as a device for burning and processing pollutants such as PCBs of this type, in Japan, a burning temperature of 1,150 ° C., a retention time of 2 seconds and an excess oxygen of 3% were tested and decomposed. The efficiency was 99.9999%, that is, the confirmation of 6-nine was the minimum requirement for implementing the device.
【0003】[0003]
【発明が解決しようとする課題】したがって、このよう
な条件を満たすためには燃焼装置は大型化が余儀なくさ
れ、能率的,効果的な装置の開発が広く望まれていた。Therefore, in order to satisfy such conditions, the combustion apparatus must be upsized, and it has been widely desired to develop an efficient and effective apparatus.
【0004】[0004]
【課題を解決するための手段】すなわち、この発明は、
PCBなどの廃油を所望燃焼油と併用または単独で供給
し、かつ微少粒噴霧状に拡分散できる廃油物質供給装置
の廃油ノズルを、燃焼炉本体の一端中央に開口接続し、
前記廃油ノズルの外周に高温高熱空気流の環状筒を設
け、かつこの環状筒の前部に斜め中心方向に向かう多数
の突出小筒を環状に並設して渦巻高熱空気送風部を形成
し前記廃油ノズルの前方で渦巻高熱燃焼領域を形成して
微少粒噴霧化した前記廃油物質を燃焼するようにしたこ
とを特徴とする廃油燃焼装置に係り、PCBのような有
害汚染物質を完全に燃焼させて無害化するようにするこ
とを目的とする。That is, the present invention is
A waste oil nozzle of a waste oil substance supply device that can supply waste oil such as PCB together with a desired combustion oil or alone and can spread and disperse it in the form of fine particles is connected to the center of one end of the combustion furnace body by opening connection.
An annular cylinder for high-temperature and high-heat air flow is provided on the outer periphery of the waste oil nozzle, and a large number of projecting small cylinders directed obliquely toward the center of the annular cylinder are annularly arranged side by side to form a spiral high-heat air blower. A swirl high heat combustion region is formed in front of a waste oil nozzle so that the waste oil substance atomized into fine particles is burned, and a waste pollutant such as PCB is completely burned. The purpose is to make it harmless.
【0005】[0005]
【作用】筒状燃焼炉の一端中央に臨まれる廃油ノズルよ
り微小の噴霧化された廃油物質は、このノズル外周の配
設された環状筒内に供給され、かつ、多数の突出小筒よ
り斜め中心方向に向かって放出される。渦巻状の高温高
熱空気により短時間にしかも有効な燃焼温度に達した状
態で燃焼処理され完全に酸化分解され、ここに有害物質
を無害化することができる。The fine atomized waste oil substance from the waste oil nozzle facing the center of one end of the tubular combustion furnace is supplied into the annular cylinder provided around the outer periphery of the nozzle, and is slanted from many protruding small cylinders. It is emitted toward the center. The vortex-shaped high-temperature, high-heat air is burnt in a short time and while reaching an effective combustion temperature, and is completely oxidized and decomposed, so that harmful substances can be rendered harmless.
【0006】[0006]
【実施例】図面について、この発明の一実施例を説明す
る。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described with reference to the drawings.
【0007】1は燃焼炉本体、2はこの炉本体1の一端
中央に開口接続したPCBなどの廃油ノズルで、廃油単
独または灯油などの燃料油と必要に応じて混合させるコ
ントローラを介して接続してある。3はこの廃油ノズル
2の外周に環状に配設される環状筒で、高温高熱空気の
供給口4が設けてある。5は前記環状筒3の前部に斜め
中心方向に向かう多数の突出小筒5aを有する渦巻高熱
空気送風部であって、廃油ノズル2の前方に渦巻高熱燃
焼領域Aを形成している。6は、この領域Aを補償しか
つこの領域A内の燃焼気体をさらに前方の燃焼炉本体1
内で旋回流を付勢させることができる放射状の傾斜フィ
ン7を有する旋回翼体であって、図示では中央に前記領
域Aに向かう膨出部8を備えるが、この構成はなくても
良い。Reference numeral 1 is a combustion furnace body, 2 is a waste oil nozzle such as PCB, which is open-connected to the center of one end of the furnace body 1, and is connected via a controller for mixing waste oil alone or fuel oil such as kerosene as needed. There is. Reference numeral 3 denotes an annular cylinder which is annularly arranged on the outer circumference of the waste oil nozzle 2 and has a supply port 4 for high temperature and high temperature air. Reference numeral 5 denotes a swirl high-heat air blower having a large number of projecting small cylinders 5a in the front part of the annular cylinder 3 and extending obliquely toward the center, and forms a spiral high-heat combustion region A in front of the waste oil nozzle 2. Reference numeral 6 denotes a combustion furnace main body 1 which compensates for this region A and further advances the combustion gas in this region A further forward.
A swirl vane having a radial inclined fin 7 capable of energizing a swirl flow therein, and a swollen portion 8 toward the region A is provided at the center in the figure, but this configuration is not necessary.
【0008】なお、全体の構成を示す図4において、9
はこの燃焼炉本体1連続して設けられるU字状の燃焼炉
道、10は排煙筒部、11は排煙筒部10内に配設され
る高温取出用の配管で廃棄物質の低温化を図っている。
12は空気層、13は耐火セラミックである。In FIG. 4, which shows the overall structure, 9
This is a U-shaped combustion furnace passage that is continuously provided in the combustion furnace body 1, 10 is a smoke exhaust tube portion, and 11 is a high temperature extraction pipe provided in the smoke exhaust tube portion 10 for lowering the temperature of waste substances. ing.
12 is an air layer and 13 is a refractory ceramic.
【0009】ところで、廃油としてのPCBは、ポリ塩
化ビフェニルと呼ばれる化学組成物であって、物理的性
質の優れ、化学的に安定であることから各種電気部品、
例えばトランス,コンデンサーなどの絶縁油とか熱媒体
などにかって広く利用されたことがある。By the way, PCB as waste oil is a chemical composition called polychlorinated biphenyl, which has excellent physical properties and is chemically stable.
For example, it has been widely used for insulating oil such as transformers and condensers and heat medium.
【0010】ところが、このPCBは、体内で取り込ま
れると分解が遅く長期間残留して毒性を発揮し、ことに
動物への投与は、肝臓において種々の薬物を代謝する酵
素を誘導することが分っており、所謂、地球環境を破壊
する汚染物質して、不用品中のPCBを燃焼して分解さ
せるなどの処理が必要であると云われている。However, this PCB, when taken up in the body, slowly decomposes and remains for a long time to exert toxicity, and it is known that administration to animals induces enzymes that metabolize various drugs in the liver. Therefore, it is said that it is necessary to treat the PCB in the waste by burning it as a so-called pollutant that destroys the global environment.
【0011】例えば、テトラクロロビフェニルの高温加
熱による酸化分解は 2C12H6 Cl4 +25O2 →24CO2 +8HCl+2H2 O……(1) で示される。For example, the oxidative decomposition of tetrachlorobiphenyl by heating at high temperature is represented by 2C 12 H 6 Cl 4 + 25O 2 → 24CO 2 + 8HCl + 2H 2 O (1).
【0012】そして、この(1)式に示される分解過程
を有効に行わせるためには、PCBの噴霧粒径は、体面
積平均径で40〜60μmで最大径は200μmをこえ
ないものが好ましいとされ、炉内に噴霧された液状のP
CB廃油の微粒子は、高温雰囲気で蒸発,分解,燃焼す
ると考えられる。したがって、最大粒径の蒸発分解速度
が炉の大きさを決定する因子となり、液滴の火炎中にお
ける粒子の変化式として次式が経験的に使用されてい
る。In order to effectively carry out the decomposition process represented by the formula (1), it is preferable that the sprayed particle diameter of PCB is 40 to 60 μm in average body area and the maximum diameter is not more than 200 μm. Liquid P atomized in the furnace
The fine particles of CB waste oil are considered to evaporate, decompose and burn in a high temperature atmosphere. Therefore, the evaporative decomposition rate of the maximum particle size becomes a factor that determines the size of the furnace, and the following formula is empirically used as a formula for changing particles in the flame of droplets.
【0013】Xt 2=XO 2−Ct ……(2) XO :最初の粒径(mm) Xt :t時間の粒径(mm) t:時間(s) C:燃焼速度定数0.7〜1.0(mm2 /s) この(2)式から、廃油PCBの噴霧最大粒径200μ
m=XO としてXt =0、すなわち完全に気化する時間
を求めてみると、1,400℃で0.04〜0.06s
の短時間に完了することになる。X t 2 = X O 2 -Ct (2) X O : initial particle size (mm) X t : particle size at t time (mm) t: time (s) C: burning rate constant 0 0.7 to 1.0 (mm 2 / s) From this equation (2), the maximum sprayed particle size of waste oil PCB is 200μ.
Assuming that m = X O , X t = 0, that is, the time required for complete vaporization is 0.04 to 0.06 s at 1,400 ° C.
Will be completed in a short time.
【0014】また、気化下PCBの熱分解に関し目的と
する分解効率ηを得るのに必要な分解時間tは t=−1n(1−η)/Ku ……(3) で示されることが分っている。The decomposition time t required to obtain the desired decomposition efficiency η for the thermal decomposition of PCB under vaporization is expressed by t = -1n (1-η) / K u (3) I know.
【0015】そしてこの(3)式に基づいて計算したP
CBの温度と目的とする分解効率に達するまでの時間と
の関係を表1に示す。Then, P calculated based on the equation (3)
Table 1 shows the relationship between the temperature of CB and the time required to reach the desired decomposition efficiency.
【0016】[0016]
【表1】 [Table 1]
【0017】上述に示す特殊なPCBの燃焼環境に立脚
して、以下にこの一実施例について、その作用を説明す
る。Based on the above-described special PCB combustion environment, the operation of this embodiment will be described below.
【0018】廃油としてのPCBを、まず灯油と混合し
て廃油ノズル2より炉本体1内に噴射分散させる。PCB as waste oil is first mixed with kerosene and sprayed from the waste oil nozzle 2 into the furnace body 1.
【0019】なお、炉本体1内は、予め400℃〜80
0℃に加熱された高温加熱空気流で十分加熱されてお
り、環状筒3より渦巻高熱空気送風部5を形成する中心
方向に傾斜した環状の多数の突出小筒5を経て、高熱空
気流が中心方向に吐出されるので、噴霧された微少粒噴
霧状の廃油PCBは、渦巻高熱燃焼領域Aで蒸発,分解
燃焼処理される。The inside of the furnace body 1 is 400 ° C. to 80 ° C. in advance.
It is sufficiently heated by the high-temperature heating air flow heated to 0 ° C., and the high-heat air flow passes through a large number of projecting small cylinders 5 of an annular shape that form the spiral high-heat air blowing part 5 inclined toward the center from the annular cylinder 3. Since it is discharged toward the center, the sprayed waste oil PCB in the form of fine particles is vaporized and decomposed in the spiral high heat combustion region A.
【0020】その時の温度は前記表1で示されるように
分解効率ηが6−nine,7−nine,8−nin
eによって異なるが例えば分解効率が6−nineであ
れば、1400℃の時、約6/1000秒の滞溜時間で
あることが必要であり、また同じ分解効率の場合、10
00℃では約1.2秒,1200℃では6/100秒の
滞溜時間を必要とすることがわかる。At that time, as shown in Table 1, the decomposition efficiency η is 6-nine, 7-nine, 8-nin.
Depending on e, for example, if the decomposition efficiency is 6-nine, it is necessary that the retention time is about 6/1000 seconds at 1400 ° C., and if the decomposition efficiency is the same, 10
It can be seen that a retention time of about 1.2 seconds at 00 ° C and 6/100 seconds at 1200 ° C is required.
【0021】この炉本体1内の全温度および滞溜時間
は、炉本体1内に設けた温度センサおよび炉本体1の口
径および高温加熱空気の送風量および次段の旋回翼体7
の流体抵抗値などより検知計測できるので、表1の条件
を設定して有効な燃焼作用を行うものである。The total temperature and staying time in the furnace main body 1 are determined by the temperature sensor provided in the furnace main body 1, the diameter of the furnace main body 1, the blowing amount of the high-temperature heated air, and the swirling blade body 7 of the next stage.
Since it can be detected and measured from the fluid resistance value of No. 1, etc., the conditions of Table 1 are set to perform effective combustion action.
【0022】このような渦巻高熱燃焼領域Aでの有効な
燃焼処理を受けた気体は、次段の旋回翼体7によってさ
らに旋回傾向を促進されU字状の燃焼炉道9より排煙筒
部10を経て大気中に放出される。The gas that has been subjected to the effective combustion treatment in the spiral high-heat combustion region A is further promoted in the swirling tendency by the swirling vane body 7 in the next stage, and the smoke exhaust tube portion 10 is discharged from the U-shaped combustion furnace passage 9. And then released into the atmosphere.
【0023】大気中には前式(1)に酸化分解されて放
出されるのでCO2 およびHClはこれを既存の回収手
段で有効に捕捉できる。[0023] Since CO 2 and HCl are released into the atmosphere after being oxidatively decomposed according to the above formula (1), CO 2 and HCl can be effectively captured by existing recovery means.
【0024】[0024]
【発明の効果】この発明によれば、PCBのような分解
しにくい廃油を、微少粒に噴霧状に拡分散させて100
0℃以上の渦巻高熱燃焼領域A内において、所望時間蒸
発,分解,燃焼を効率よく行わせているので完全な熱分
解が行われ、ここに完全な無害化状態にすることができ
る。EFFECTS OF THE INVENTION According to the present invention, waste oil which is not easily decomposed, such as PCB, is dispersed in fine particles in a spray form to obtain 100
In the spiral high heat combustion region A of 0 ° C. or higher, evaporation, decomposition and combustion are efficiently performed for a desired time, so that complete thermal decomposition is performed and a complete detoxified state can be obtained.
【図1】 この発明に係る廃油燃焼装置の要部の拡大断
面図FIG. 1 is an enlarged sectional view of a main part of a waste oil combustion device according to the present invention.
【図2】 同上A−A線断面図FIG. 2 is a sectional view taken along line AA of the above.
【図3】 図1のB−B線断面図FIG. 3 is a sectional view taken along line BB of FIG.
【図4】 全体の説明断面図FIG. 4 is an explanatory sectional view of the whole.
A 渦巻高熱燃焼領域 1 燃焼炉本体 2 廃油ノズル 3 環状筒 5 渦巻高熱空気送風部 5a 突出小筒 7 旋回翼体 A swirl high heat combustion area 1 combustion furnace body 2 waste oil nozzle 3 annular cylinder 5 spiral high heat air blower 5a protruding small cylinder 7 swirl vane
Claims (1)
たは単独で供給し、かつ微少粒噴霧状に拡分散できる廃
油物質供給装置の廃油ノズルを、燃焼炉本体の一端中央
に開口接続し、前記廃油ノズルの外周に高温高熱空気流
の環状筒を設け、かつこの環状筒の前部に斜め中心方向
に向かう多数の突出小筒を環状に並設して渦巻高熱空気
送風部を形成し前記廃油ノズルの前方で渦巻高熱燃焼領
域を形成して微少粒噴霧化した前記廃油物質を燃焼する
ようにしたことを特徴とする廃油燃焼装置。1. A waste oil nozzle of a waste oil substance supply device capable of supplying waste oil such as PCB together with a desired combustion oil or by itself and spreading and dispersing in a fine particle spray form, is open-connected to one end center of a combustion furnace main body, An annular cylinder for high-temperature and high-heat air flow is provided on the outer periphery of the waste oil nozzle, and a large number of projecting small cylinders directed obliquely toward the center of the annular cylinder are annularly arranged side by side to form a spiral high-heat air blower. A waste oil combustion apparatus, characterized in that a swirl high heat combustion region is formed in front of the waste oil nozzle to burn the waste oil substance atomized into fine particles.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5229067A JP2540717B2 (en) | 1993-09-14 | 1993-09-14 | Waste oil combustion equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5229067A JP2540717B2 (en) | 1993-09-14 | 1993-09-14 | Waste oil combustion equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0783425A true JPH0783425A (en) | 1995-03-28 |
JP2540717B2 JP2540717B2 (en) | 1996-10-09 |
Family
ID=16886222
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP5229067A Expired - Fee Related JP2540717B2 (en) | 1993-09-14 | 1993-09-14 | Waste oil combustion equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2540717B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102042588A (en) * | 2010-10-11 | 2011-05-04 | 无锡华光锅炉股份有限公司 | Air supply structure of oil gun under bed of circulating fluidized bed boiler |
-
1993
- 1993-09-14 JP JP5229067A patent/JP2540717B2/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102042588A (en) * | 2010-10-11 | 2011-05-04 | 无锡华光锅炉股份有限公司 | Air supply structure of oil gun under bed of circulating fluidized bed boiler |
Also Published As
Publication number | Publication date |
---|---|
JP2540717B2 (en) | 1996-10-09 |
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Legal Events
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A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 19960326 |
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LAPS | Cancellation because of no payment of annual fees |