JPH03260512A - Incinerator and method of igniting radioactive waste material - Google Patents
Incinerator and method of igniting radioactive waste materialInfo
- Publication number
- JPH03260512A JPH03260512A JP2059339A JP5933990A JPH03260512A JP H03260512 A JPH03260512 A JP H03260512A JP 2059339 A JP2059339 A JP 2059339A JP 5933990 A JP5933990 A JP 5933990A JP H03260512 A JPH03260512 A JP H03260512A
- Authority
- JP
- Japan
- Prior art keywords
- combustion
- incinerator
- air
- oxygen
- igniting
- 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
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
Landscapes
- Incineration Of Waste (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は原子力施設から発生する可燃性の雑固体廃棄物
等を焼却するのに適した焼却炉およびこれを用いた放射
性廃棄物の焼却方法に関するものである。Detailed Description of the Invention (Field of Industrial Application) The present invention provides an incinerator suitable for incinerating combustible miscellaneous solid waste generated from nuclear facilities, and a method for incinerating radioactive waste using the incinerator. It is related to.
(従来の技術)
原子力発電所のような原子力施設から発生する可燃性の
雑固体廃棄物は従来から焼却炉により焼却処理されてい
るが、この場合にはポリエチレン、紙、布等の可燃物の
専焼のみではなく、ゴム、廃樹脂、スラッジ等の難燃物
との混焼も行われている。ところがこのような難燃物と
の混焼を行うと未燃物や煤等が発生して後工程の排ガス
処理設備の負担が増えるため、混焼比は低く抑えられて
いた。またこのような従来の焼却炉はフィルタ、ブロア
等を含む大規模な排ガス処理設備を必要としており、設
備コストが高いうえメンテナンスの費用も高くつく問題
があった。(Prior technology) Combustible miscellaneous solid waste generated from nuclear facilities such as nuclear power plants has traditionally been incinerated in incinerators, but in this case, combustible materials such as polyethylene, paper, cloth, etc. In addition to exclusive combustion, mixed combustion with flame retardants such as rubber, waste resin, and sludge is also carried out. However, co-firing with such flame retardants generates unburnt materials, soot, etc., which increases the burden on exhaust gas treatment equipment in subsequent processes, so the co-firing ratio has been kept low. In addition, such conventional incinerators require large-scale exhaust gas treatment equipment including filters, blowers, etc., resulting in high equipment costs and high maintenance costs.
(発明が解決しようとする課題〉
本発明は上記した従来の問題点を解決して、難燃物との
混焼比を高めることができる優れた燃焼性を持ち、また
焼却炉および排ガス処理設備の設備容量を低減すること
ができる焼却炉およびこれを用いた放射性廃棄物の焼却
方法を提供するために完成されたものである。(Problems to be Solved by the Invention) The present invention solves the above-mentioned conventional problems, has excellent combustibility that can increase the co-combustion ratio with flame retardants, and This was completed in order to provide an incinerator that can reduce equipment capacity and a method of incinerating radioactive waste using the incinerator.
(課題を解決するための手段)
上記の課題は、廃棄物を焼却するための炉本体に、25
〜40%の酸素濃度の空気を燃焼空気および強燃空気と
して供給する富酸素供給設備と、燃焼部に水を噴霧する
スチームインジェクション設備とを付設したことを特徴
とする焼却炉によって解決される。(Means for solving the problem) The above problem is that the furnace body for incinerating waste has a
This problem is solved by an incinerator characterized by being equipped with oxygen-enriched supply equipment that supplies air with an oxygen concentration of ~40% as combustion air and flammable air, and steam injection equipment that sprays water into the combustion section.
また上記の課題は、上記構造の焼却炉に放射性廃棄物を
投入し、水を噴霧することにより排ガス温度を1000
℃以下に制御しつつ燃焼させることを特徴とする放射性
廃棄物の焼却方法によって解決される。In addition, the above problem was solved by putting radioactive waste into an incinerator with the above structure and spraying water to reduce the exhaust gas temperature to 1,000 yen.
The problem is solved by a method of incinerating radioactive waste, which is characterized by burning while controlling the temperature below ℃.
(実施例) 以下に本発明を図面を参照しつつ更に詳細に説明する。(Example) The present invention will be explained in more detail below with reference to the drawings.
図中、(1)は放射性廃棄物等の廃棄物を焼却するため
の炉本体であり、この炉本体(1)には25〜40%の
酸素濃度の空気を燃焼空気および強燃空気として供給す
る富酸素供給設備(2)が付設されている。In the figure, (1) is the furnace body for incinerating waste such as radioactive waste, and air with an oxygen concentration of 25 to 40% is supplied to this furnace body (1) as combustion air and flammable air. An oxygen-enriched supply facility (2) is attached.
富酸素供給設備(2)としては例えば酸素富化膜を使用
することができ、燃焼空気供給路(3)および強燃空気
供給路(4)を介して炉本体(1)の燃焼部に富酸素空
気を供給している。このように酸素濃度の高い空気を供
給することにより燃焼性が向上し、難燃物との混焼比を
高めることができるようになるが、酸素濃度が25%未
満であると普通の空気を用いている通常の焼却炉の燃焼
性との差が不十分であり、逆に酸素濃度が40%を越え
ると燃焼温度が高くなり過ぎるので、25〜40%の酸
素濃度の空気が適当である。As the oxygen-enriched supply equipment (2), for example, an oxygen-enriched membrane can be used, and the oxygen-enriched membrane is supplied to the combustion section of the furnace body (1) via the combustion air supply path (3) and the flammable air supply path (4). Supplying oxygen air. By supplying air with a high oxygen concentration in this way, combustibility improves and it becomes possible to increase the co-combustion ratio with flame retardants, but if the oxygen concentration is less than 25%, ordinary air is used. The difference in combustibility from that of a normal incinerator is insufficient, and on the other hand, if the oxygen concentration exceeds 40%, the combustion temperature will become too high, so air with an oxygen concentration of 25 to 40% is appropriate.
(5)は炉本体(1)の燃焼部に水を噴霧することがで
きるスチームインジェクション設備である。このスチー
ムインジェクション設備は炉内に設置されたノズルから
燃焼空気量の115〜l/20程度の水を噴霧するもの
で、噴霧された水の蒸発潜熱により燃焼部の温度を低下
させ、噴霧量の調節によって排ガス温度が1ooo″C
以下に保たれるように制御する。ここで排ガス温度を1
000℃以下としたのは、これより高温になると耐火れ
んがの膨脂収縮によるクランク、割れの発生が激しく、
寿命が短縮されるとともに炉内の温度測定器、制御機器
等への影響が大きくなるためである。(5) is a steam injection equipment that can spray water into the combustion part of the furnace body (1). This steam injection equipment sprays water at an amount of about 115 to 20 l/20 of the amount of combustion air from a nozzle installed in the furnace.The latent heat of vaporization of the sprayed water lowers the temperature of the combustion section, reducing the amount of spray. Adjustment reduces exhaust gas temperature to 1ooo''C
Control to maintain the following. Here, the exhaust gas temperature is 1
The reason for setting the temperature below 000℃ is that at higher temperatures, cracks and cracks will occur more frequently due to expansion and contraction of the refractory bricks.
This is because the lifespan is shortened and the influence on the temperature measuring device, control equipment, etc. inside the furnace is increased.
(6)はフィルタ(7)と排ガスブロア(8)とを含む
排ガス処理設備である。炉内の燃焼ガスはフィルタ(7
)により放射性物質等を完全に除塵されたうえ、排ガス
ブロア(8)により糸外へ放出される。(6) is exhaust gas treatment equipment including a filter (7) and an exhaust gas blower (8). The combustion gas in the furnace is filtered through a filter (7
) to completely remove radioactive substances, etc., and then discharged to the outside of the thread by an exhaust gas blower (8).
(作用)
このように槽底された本発明の焼却炉においては、富酸
素供給設備(2)により炉本体(1)に25〜40%の
酸素濃度の空気が燃焼空気として供給される。(Function) In the incinerator of the present invention having the tank bottom as described above, air having an oxygen concentration of 25 to 40% is supplied as combustion air to the furnace body (1) by the oxygen-enriched supply equipment (2).
そして放射性廃棄物のうち、ポリエチレン、紙、布等の
島燃物と、ゴム、廃樹脂、スラッジ等の難燃物との混焼
を行った場合に発生する分解ガスおよび煤の気相中の燃
焼速度は酸素濃度に比例して増加して燃焼性が向上する
ので、難燃物との混焼を行っても多量の未燃物や煤等を
発生させることなく速やかに燃焼させることができ、併
せて排ガス量の低減を図ることができる。なお、ゴム等
の酸素指数(燃焼性を表す指標で酸素濃度を示す)が3
0〜40であるところから燃焼性の向上と排ガス量の低
減のためには富酸素空気の酸素濃度は高い程よいが、前
述したように酸素濃度が高過ぎると炉内温度や排ガス温
度の過度の上昇を招くので、25〜40%の範囲が好ま
しい。Among radioactive wastes, combustion of decomposed gas and soot in the gas phase occurs when co-combustion of combustible materials such as polyethylene, paper, and cloth with flame retardant materials such as rubber, waste resin, and sludge. The speed increases in proportion to the oxygen concentration, improving combustibility, so even if co-fired with flame retardants, it can be quickly combusted without producing a large amount of unburned materials or soot. Therefore, it is possible to reduce the amount of exhaust gas. Please note that the oxygen index (an indicator of flammability that indicates oxygen concentration) of rubber, etc. is 3.
0 to 40, so the higher the oxygen concentration in the oxygen-enriched air, the better in order to improve combustibility and reduce the amount of exhaust gas, but as mentioned above, if the oxygen concentration is too high, the temperature inside the furnace and the exhaust gas temperature will rise excessively. A range of 25 to 40% is preferable since this causes an increase in the amount of water.
また本発明の焼却炉においては、スチームインジェクシ
ョン設備(5)により燃焼部に水が噴霧され、これによ
って排ガス温度の低下と溶融した焼却物の炉壁への付着
が防止される。その供給量はポリエチレンのような高発
熱量物の燃焼の場合には燃焼空気量の115程度、含水
物のような低発熱量物の燃焼で排ガス温度の上昇が小さ
い場合には、燃焼空気量のl/20程度とすればよく、
平均的には1710前後とすればよい。このようにして
排ガス温度を1000″C以下に制御しつつ燃焼が行わ
れ、排ガスは排ガス処理設置(6)により浄化されたう
えで系外へ放出される。Furthermore, in the incinerator of the present invention, water is sprayed into the combustion section by the steam injection equipment (5), thereby reducing the exhaust gas temperature and preventing molten incineration material from adhering to the furnace wall. The supply amount is approximately 115 of the amount of combustion air in the case of combustion of a high calorific value such as polyethylene, and the amount of combustion air when the rise in exhaust gas temperature is small due to the combustion of a low calorific value such as a water-containing material. It should be about l/20 of
On average, it should be around 1710. In this way, combustion is performed while controlling the exhaust gas temperature to 1000''C or less, and the exhaust gas is purified by the exhaust gas treatment installation (6) and then released to the outside of the system.
上記した本発明の作用をit認するため、酸素富化膜に
より富酸素空気を供給する本発明の方法による焼却試験
と、通常空気による従来法の焼却試験を実施した。In order to confirm the effects of the present invention described above, an incineration test using the method of the present invention in which oxygen-enriched air is supplied using an oxygen-enriched membrane, and an incineration test using a conventional method using normal air were conducted.
試験装置は定格処理容量が10kgの雑固体焼却炉であ
り、供試試料としては原子力発電所で一般的に発生する
可燃性雑固体廃棄物の模擬廃棄物である、ポリエチレン
、ウェス、濡れウェス (水分50%)を15:1:4
の割合で混合したものを200gずつ袋詰めにしたもの
を使用した。そして燃焼空気の流量は、酸素濃度が27
%の富酸素空気の場合には14ON%/h、酸素濃度が
21%の通常空気の場合には18ON rrr /hと
し、焼却時間はいずれも3時間、焼却開始時の炉下部の
温度は約900°C1−次セラミックフィルタの部分で
測定した排ガス温度は700〜750°Cであった。ま
たスチームインジェクシゴン設置(5)により燃焼部に
燃焼空気の1710の水が噴霧された。The test equipment is a miscellaneous solid waste incinerator with a rated processing capacity of 10 kg, and the test samples are polyethylene, rags, and wet rags (which are simulated combustible miscellaneous solid wastes commonly generated at nuclear power plants). 50% water) to 15:1:4
A mixture of 200 g of each bag was used. And the flow rate of combustion air is such that the oxygen concentration is 27
% oxygen-rich air, 14ON%/h, and normal air with an oxygen concentration of 21%, 18ON rrr/h.The incineration time was 3 hours in both cases, and the temperature at the bottom of the furnace at the start of incineration was approximately The exhaust gas temperature measured at the 900°C primary ceramic filter was 700-750°C. Also, 1710 water of combustion air was sprayed into the combustion section by installing a steam injector (5).
その結果、本発明法によれば排ガス処理段# (6)へ
の負担率は従来法の70%にまで減少した。また本発明
法によれば焼却残渣量が33gであって従来法の場合の
59gに比較して大幅に減少し、残塩時間も従来が18
分であったのに比較して8分と大幅に減少した。更に本
発明法によれば炉出口における排ガス中のダスト濃度が
従来の0.02〜0.1g/N+dに比較して0.00
4〜0.02 g/Nrrrと一桁低くなり、燃焼性が
著しく向上したことがn認された。As a result, according to the method of the present invention, the load on exhaust gas treatment stage # (6) was reduced to 70% of the conventional method. In addition, according to the method of the present invention, the amount of incineration residue is 33g, which is significantly reduced compared to 59g in the case of the conventional method, and the residual salt removal time is 18g compared to the conventional method.
This is a significant decrease of 8 minutes compared to the previous 8 minutes. Furthermore, according to the method of the present invention, the dust concentration in the exhaust gas at the furnace outlet is 0.00 compared to the conventional 0.02 to 0.1 g/N+d.
It was found that the combustibility was significantly improved by an order of magnitude lower than 4 to 0.02 g/Nrrr.
(発明の効果) 本発明の効果を要約すると次の通りである。(Effect of the invention) The effects of the present invention are summarized as follows.
■ 本発明は富酸素燃焼法の採用により分解ガスや煤の
燃焼速度を向上させることができ、煤等の低減と燃焼性
の向上を図ることができる。例えば、酸素濃度を27%
とすることにより、煤の発生量をl/10とすることが
できる。(2) The present invention can improve the combustion rate of cracked gas and soot by adopting an oxygen-enriched combustion method, and can reduce soot and the like and improve combustibility. For example, increase the oxygen concentration to 27%
By doing so, the amount of soot generated can be reduced to 1/10.
■ 本発明によれば、水分含有物や低発熱量物のような
難燃物をも容易に焼却することができ、これらの混焼比
を増加させることができる。(2) According to the present invention, it is possible to easily incinerate even flame retardant materials such as water-containing materials and materials with low calorific value, and the co-combustion ratio of these materials can be increased.
■ 本発明によれば富酸素燃焼法の採用により排ガス量
の減少を図ることができるので、焼却炉および排ガス処
理設備の容量の低減を図ることができる。具体的には、
酸素濃度を30%とし、低発熱置物専焼の場合には、炉
容量を50%、排ガス処理設備の容量を70%とするこ
とができる。また酸素濃度が同一で高発熱置物専焼の場
合(温度過上昇の厳しい条件の場合)には、水の供給量
を燃焼空気の175 とすることにより、炉容量を74
%、排ガス処理設備の容量を85%とすることができる
。(2) According to the present invention, the amount of exhaust gas can be reduced by adopting the oxygen-enriched combustion method, so the capacity of the incinerator and exhaust gas treatment equipment can be reduced. in particular,
When the oxygen concentration is 30% and low heat generation ornaments are exclusively fired, the furnace capacity can be 50% and the capacity of the exhaust gas treatment equipment can be 70%. In addition, when the oxygen concentration is the same and high heat generation figurines are exclusively fired (under severe conditions of excessive temperature rise), the furnace capacity can be increased to 74% by setting the water supply amount to 175% of the combustion air.
%, and the capacity of the exhaust gas treatment equipment can be made 85%.
■ 本発明によれば、スチームインジエクシテン設備か
らの水の供給により、排ガス温度の過度の上昇による炉
壁の耐火れんがへの影響(寿命短縮)や焼却物の溶融に
よる炉壁への固着を防止することができる。よって本発
明は従来の問題点を解消した焼却炉およびこれを用いた
放射性廃棄物の焼却方法として、産業の発展に寄与する
ところはきわめて大きいものである。■According to the present invention, by supplying water from the steam injector equipment, the influence of excessive rise in exhaust gas temperature on the refractory bricks on the furnace wall (shortening of life) and the sticking of incinerated materials to the furnace wall due to melting can be prevented. It can be prevented. Therefore, the present invention greatly contributes to the development of industry as an incinerator that solves the problems of the conventional incinerator and a method of incinerating radioactive waste using the incinerator.
図面は本発明の実施例を示す概略的な断面図である。
(1):炉本体、(2):富酸素供給設備、(5):ス
チームインジェクシヲン設備。
1:・大肪祷 2糧輪1杖め川西
5:スナー医インジシフ力ン1賢へ粕The drawings are schematic cross-sectional views showing embodiments of the invention. (1): Furnace body, (2): Oxygen-enriched supply equipment, (5): Steam injection equipment. 1: Great prayer 2 bread wheels 1 cane Kawanishi 5: Snar doctor injishifu power 1 wise man lees
Claims (1)
0%の酸素濃度の空気を燃焼空気および残燃空気として
供給する富酸素供給設備(2)と、燃焼部に水を噴霧す
るスチームインジェクション設備(5)とを付設したこ
とを特徴とする焼却炉。 2、請求項1記載の焼却炉に放射性廃棄物を投入し、水
を噴霧することにより排ガス温度を1000℃以下に制
御しつつ燃焼させることを特徴とする放射性廃棄物の焼
却方法。[Claims] 1. The furnace body (1) for incinerating waste has 25 to 4
An incinerator characterized by being equipped with oxygen-enriched supply equipment (2) that supplies air with an oxygen concentration of 0% as combustion air and residual combustion air, and steam injection equipment (5) that sprays water into the combustion section. . 2. A method for incinerating radioactive waste, comprising charging the radioactive waste into the incinerator according to claim 1, and burning the waste while controlling the exhaust gas temperature to 1000° C. or less by spraying water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2059339A JPH03260512A (en) | 1990-03-09 | 1990-03-09 | Incinerator and method of igniting radioactive waste material |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2059339A JPH03260512A (en) | 1990-03-09 | 1990-03-09 | Incinerator and method of igniting radioactive waste material |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH03260512A true JPH03260512A (en) | 1991-11-20 |
Family
ID=13110460
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2059339A Pending JPH03260512A (en) | 1990-03-09 | 1990-03-09 | Incinerator and method of igniting radioactive waste material |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH03260512A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2015072132A (en) * | 2013-10-01 | 2015-04-16 | 日本碍子株式会社 | Radioactive waste volume reduction treatment apparatus and volume reduction treatment method |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5611552Y2 (en) * | 1977-03-09 | 1981-03-16 | ||
| JPS60176409A (en) * | 1984-02-23 | 1985-09-10 | 松下電工株式会社 | Wiring implement |
| JPH0210718U (en) * | 1988-06-30 | 1990-01-23 | ||
| JPH0236712A (en) * | 1988-07-26 | 1990-02-06 | Matsushita Electric Works Ltd | Plate frame for wiring fixture |
| JPH028483Y2 (en) * | 1982-05-31 | 1990-02-28 |
-
1990
- 1990-03-09 JP JP2059339A patent/JPH03260512A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5611552Y2 (en) * | 1977-03-09 | 1981-03-16 | ||
| JPH028483Y2 (en) * | 1982-05-31 | 1990-02-28 | ||
| JPS60176409A (en) * | 1984-02-23 | 1985-09-10 | 松下電工株式会社 | Wiring implement |
| JPH0210718U (en) * | 1988-06-30 | 1990-01-23 | ||
| JPH0236712A (en) * | 1988-07-26 | 1990-02-06 | Matsushita Electric Works Ltd | Plate frame for wiring fixture |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2015072132A (en) * | 2013-10-01 | 2015-04-16 | 日本碍子株式会社 | Radioactive waste volume reduction treatment apparatus and volume reduction treatment method |
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