JPS60174419A - Method of processing waste liquid from calcining furnace - Google Patents
Method of processing waste liquid from calcining furnaceInfo
- Publication number
- JPS60174419A JPS60174419A JP2718684A JP2718684A JPS60174419A JP S60174419 A JPS60174419 A JP S60174419A JP 2718684 A JP2718684 A JP 2718684A JP 2718684 A JP2718684 A JP 2718684A JP S60174419 A JPS60174419 A JP S60174419A
- Authority
- JP
- Japan
- Prior art keywords
- fluidized bed
- waste liquid
- heater
- temperature
- furnace
- 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
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/008—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for liquid waste
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/30—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed
Abstract
Description
【発明の詳細な説明】
本発明は、廃液を処理する流動層式燻焼炉の廃液処理法
に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating waste liquid from a fluidized bed smoker.
従来、流動層式燻焼炉は、廃液等の;段焼処理に要する
熱源を流動化ガスの保有熱に依存していた。Conventionally, fluidized bed smoking furnaces have relied on the heat retained in fluidizing gas as the heat source required for staged burning treatment of waste liquid and the like.
すなわち、ガスの持つエンタルピのみを利用して水分を
蒸発させていたのである。In other words, water was evaporated using only the enthalpy of the gas.
従来の飯焼炉の廃液処理法の概略を第1図に示す。Figure 1 shows an outline of a conventional method for treating waste liquid from a rice baking furnace.
図において、符号工は燻焼炉、2は風箱部、3は流動層
部、4はフリーボード部、5は分散板、6は流動層部ヒ
ータ、7は外部ヒータ、8は流動7化ガス、9は流動媒
体、1oは処理廃液、11はガス出口を示す。In the figure, the symbol is the smoking furnace, 2 is the wind box part, 3 is the fluidized bed part, 4 is the freeboard part, 5 is the distribution plate, 6 is the fluidized bed part heater, 7 is the external heater, and 8 is the fluidized bed part. 9 is a fluidizing medium, 1o is a treated waste liquid, and 11 is a gas outlet.
燻焼炉1の流動層部3に供給された処理廃液10は外部
ヒータ7により加熱された流動化ガス8と接触し、燻焼
される。しかし、一般にはこの流動化ガス8を高温に加
熱すると、処理廃液1oの性質によっては廃液中の溶質
分が溶融・固着して流動限外を起こすことがある他、分
散板5など炉の構成部材の耐熱性の問題もあシ、一定の
ガス温度以下とする必要があった。例えば、ほう酸を含
む放射性廃液を燗焼処理した場合、流動化ガス8の温度
が約550’C以上の場合に分散板5及び炉内構成物に
ほう酸塩等が溶融・固着し、フリンヵとなり、分散板5
の圧損を増大させ、最終的には流動不能となる等の不具
合が生じる。また、前記一定のガス温度以下とする必要
があることは、そのため、流動化ガス8のエンタルピは
限られ、廃液の力役焼能力を大きくとることは不可能で
あった。The treated waste liquid 10 supplied to the fluidized bed section 3 of the smoldering furnace 1 comes into contact with the fluidizing gas 8 heated by the external heater 7 and is smoldered. However, in general, when this fluidizing gas 8 is heated to a high temperature, depending on the properties of the treated waste liquid 1o, solutes in the waste liquid may melt and solidify, causing the fluidity limit to be exceeded. There was also the issue of heat resistance of the parts, and the gas temperature had to be kept below a certain level. For example, when a radioactive waste liquid containing boric acid is roasted, if the temperature of the fluidizing gas 8 is about 550'C or higher, borates and the like will melt and stick to the distribution plate 5 and the components in the furnace, forming flinkers. Dispersion plate 5
This increases the pressure loss and eventually causes problems such as impossibility of flow. Further, the need to keep the gas temperature below the above-mentioned constant value means that the enthalpy of the fluidizing gas 8 is limited, making it impossible to increase the power burning capacity of the waste liquid.
従って、燻焼炉の処理能力を増加させる場合、これ迄は
炉内径を太きぐするが、ガスの空塔速度(炉内のガス通
過速度)を速くする等、流動化ガス侶の増分により熱量
を補っていたが、この方法では排ガス量が多くなり、装
置の大型化ひいてはコストアップにつながることになる
。Therefore, when increasing the processing capacity of a smoldering furnace, the inner diameter of the furnace has been increased, but the amount of heat is However, this method increases the amount of exhaust gas, making the equipment larger and increasing costs.
本発明はこのよう々従来例の不具合に鑑みてなされたも
ので、出来るだけ小型の装置で、よシ経済的に燻焼処理
できる設備を供給することを目的とする。The present invention has been made in view of the problems of the conventional examples, and it is an object of the present invention to provide equipment that is as small as possible and can perform smoking process economically.
流動層式燻焼炉は通當炉壁の外面に約150nnnの保
温利(ケイ酸カルシウム等)が数例けられているが、本
発明は該燻焼炉の流動層部の外壁面にヒータを設け、炉
内に熱を供給できるようにすると共に、前記保温拐をも
数例けることを特徴とする。In some fluidized bed type smoking furnaces, a heat insulating material (calcium silicate, etc.) of about 150 nnn is provided on the outer surface of the furnace wall, but the present invention provides a heater on the outer wall surface of the fluidized bed portion of the smoking furnace. The furnace is characterized in that it is equipped with a heater to supply heat to the inside of the furnace, and also includes several types of heat insulation.
県下、本発明の好適な実施例につき添付図面を参照して
詳述する。DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the present invention will now be described in detail with reference to the accompanying drawings.
本発明になる燻焼炉を第2図に示す。図において、部品
省号1〜11は前記第1図と同様である。FIG. 2 shows a smoking furnace according to the present invention. In the figure, parts numbers 1 to 11 are the same as in FIG. 1 above.
11没焼炉1は大別して、風箱部2、流動層部3、フリ
ーボード部4及び風箱部2と流動層部30間に位置する
分散板5から成る。さらに本発明においては、この流動
層部3の壁面に流動層部ヒータ6を設けている。11 The infertility furnace 1 is roughly divided into a wind box part 2, a fluidized bed part 3, a freeboard part 4, and a dispersion plate 5 located between the wind box part 2 and the fluidized bed part 30. Further, in the present invention, a fluidized bed section heater 6 is provided on the wall surface of this fluidized bed section 3.
外部ヒータ7により加熱された流動化ガス8は分散板5
を通過した後、流動層内の流動媒体9を加熱、攪拌して
いる。この流動層内へ処理廃液1゜を噴霧して燻焼処理
を行なう時、処理廃液中の水分が蒸発するため、その潜
熱により流動媒体9の温度が低下する傾向にある。The fluidizing gas 8 heated by the external heater 7 passes through the distribution plate 5
After passing through the fluidized bed, the fluidized medium 9 in the fluidized bed is heated and stirred. When 1° of treated waste liquid is sprayed into this fluidized bed to carry out the smoldering process, the water in the treated waste liquid evaporates, and the temperature of the fluidized medium 9 tends to drop due to its latent heat.
この流動媒体9の温度低下を肪き、蒸発潜熱を補うため
に壁面から熱量を供給して、所定の)段焼処理を行なう
。In order to compensate for this temperature drop in the fluidized medium 9 and compensate for the latent heat of vaporization, heat is supplied from the wall surface to perform a predetermined stage baking process.
前記流動層部ヒータ6を設けることにより、流動化ガス
8の温度を低下させず、所定の燗焼処理温度に保った状
態で、処理廃液を燻焼させることが出来る効果があろう
この流動層部ヒータ6が無い場合は、流動化ガス8の持
つエンタルピで蒸発潜熱を補うために、ガス温度が下が
り、所定の処理温度を保つことが困難になる。By providing the fluidized bed section heater 6, this fluidized bed has the effect of being able to smoke the treated waste liquid while maintaining the temperature of the fluidizing gas 8 at a predetermined roasting temperature without lowering it. If the heater 6 is not provided, the enthalpy of the fluidizing gas 8 compensates for the latent heat of vaporization, which lowers the gas temperature and makes it difficult to maintain a predetermined processing temperature.
また、所定の処理温度を得るために、予め蒸発潜熱分だ
け流動化ガス温度を高くした場合は、分散板近辺の温度
が高くなり、流動媒体9が溶融し固塊物が生じることが
あり、トラブルの原因となる。Furthermore, if the temperature of the fluidizing gas is increased in advance by the amount of the latent heat of vaporization in order to obtain a predetermined processing temperature, the temperature near the dispersion plate may become high, and the fluidizing medium 9 may melt and form solids. It may cause trouble.
なお、具体例としてヒータ6の数句状況を第3図(al
、tb+に示し、放射性液体廃棄物を燻焼処理した場合
の例につき説明する2、
はう酸を主成分とし、たσ1ツ4rii廃液を処理する
場合、適正な燗焼処理温度(流動層内温度)は約300
℃〜350°Cでル)る。この1段焼処押を同一の炉内
径を持つ流動層式燻焼炉で行なう場合、流動層部ヒータ
6の有無により次の差が生じたー
すなわち、従来は蒸発潜熱をカバーするため、流動化ガ
フ8を最高限度である約500℃に加熱し、適jE処」
甲温度約300℃〜350℃との差(約150〜200
°C)を水分蒸発に充当していたーこの時の濃縮廃液の
処理能力は約25o1(濃縮廃液)7m2(流動層断面
積り・H程度であった。As a specific example, the situation of the heater 6 is shown in Figure 3 (al.
, tb+, and an example of smoking radioactive liquid waste will be explained. temperature) is approximately 300
℃~350℃. When this one-stage burning process is carried out in a fluidized bed type smoking furnace with the same inner diameter, the following difference occurs depending on the presence or absence of the fluidized bed heater 6. Heat the chemical gaff 8 to the maximum temperature of approximately 500℃ and process it appropriately.
The difference between the instep temperature of about 300℃~350℃ (about 150~200℃)
°C) was used for water evaporation - the processing capacity of the concentrated waste liquid at this time was about 25 o1 (concentrated waste liquid) 7 m2 (cross-sectional area of the fluidized bed/H).
ところが、流動層部ヒータ6を設置し、同様の燻焼処理
を実施した結果、流動化ガス温度を約300〜350°
CKして燻焼処理したにもかかわらず、処理能力は約5
0%以上、向上させることが出来た。However, as a result of installing the fluidized bed section heater 6 and performing the same smoldering process, the fluidizing gas temperature was reduced to approximately 300 to 350°.
Even though it was CKed and smoked, the processing capacity was about 5.
We were able to improve this by more than 0%.
前記適正処理湯度が300〜350℃である理由につい
て説明する。′
はう酸を含む廃液を燻焼処理する場合、一般には、この
廃液にカセイソーダが加えられ、燗焼生成物としてホウ
素とすトリウムの化合物であるホラクスN a、2 B
407・nH,、o )が主に得られる。この時のn
分子の結晶水は処理温度により異なり、10分子(常温
)から無水物(320℃)壕で変化する。The reason why the appropriate treatment hot water temperature is 300 to 350°C will be explained. ' When waste liquid containing oxalic acid is smoked, caustic soda is generally added to the waste liquid, and Horax Na,2 B, which is a compound of boron and thorium, is produced as a smoldering product.
407·nH,,o) are mainly obtained. n at this time
The molecular crystallization water varies depending on the processing temperature, and varies from 10 molecules (at room temperature) to anhydrous (320° C.).
ここでは、よシ完全な1没焼処理を行ない、かつ必要以
上の高温にしないということで、適正温度を300〜3
50°Cとしたので・ある。Here, we set the appropriate temperature to 300 to 300℃ to perform a thorough one-burning process and not to raise the temperature higher than necessary.
It is 50°C, so it is.
次にヒータ出力例について述べる。Next, an example of heater output will be described.
廃液を110 fl/ 、Hで燻焼処理する場合の燗焼
炉内径は約750mmφ、ヒータ出力は約100PWと
なる。When the waste liquid is smoked at 110 fl/H, the inner diameter of the roasting furnace is approximately 750 mmφ, and the heater output is approximately 100 PW.
この100 KWのうち、50KWはベースヒータとし
て常時使用し、残シの50KWは炉内温度を一定温度(
例、350℃)に調整すべく、燗焼処理量の変化に対応
した出力制御を行なう。Of this 100 KW, 50 KW is constantly used as a base heater, and the remaining 50 KW is used to maintain the furnace temperature at a constant temperature (
For example, in order to adjust the temperature to 350° C., output control is performed in accordance with changes in the amount of roasting.
コノ時ノ流動化カフ、 i ハ約1050 ”’ /
H、350°Cで供給され、流動層静止層高は約600
.Hである第3図の補足としてヒータ数句状況を第4図
+a+、(b)に示す。The fluidizing cuff is approximately 1050 ''/
H, supplied at 350°C, and the static bed height of the fluidized bed is approximately 600°C.
.. As a supplement to FIG. 3, which is H, the heater number situation is shown in FIG. 4+a+ and (b).
図において、符号3.5.6.10は前記図と同一部品
を示し、その他、12は管台、13は保温材、14は胴
部(シェル)、15は保温外面、16は炉内部、17は
端子箱を示す。In the figure, numerals 3, 5, 6, 10 indicate the same parts as in the previous figure, and 12 is a nozzle stand, 13 is a heat insulating material, 14 is a body (shell), 15 is a heat insulating outer surface, 16 is a furnace inside, 17 indicates a terminal box.
ヒータ6はこの例では電気ヒータで、その取付は流動層
部3にヒータ6を縦にクランプで固定する。この場合、
総本数は例として100本で割100KWの出力である
。管台12は円周上の同一方向にまとめ、残りの部分に
ヒータ6を取付ける。The heater 6 is an electric heater in this example, and is mounted by vertically fixing the heater 6 to the fluidized bed section 3 with clamps. in this case,
As an example, the total number is divided by 100 to give an output of 100KW. The nozzles 12 are grouped in the same direction on the circumference, and the heater 6 is attached to the remaining portion.
ヒータ6はクランプにより炉壁外面15に取イ」け、そ
の上に保温材13を施ず。このヒータ6及び保温材13
は取外し可能なものとする。The heater 6 is attached to the outer surface 15 of the furnace wall using a clamp, and no heat insulating material 13 is applied thereon. This heater 6 and heat insulating material 13
shall be removable.
第1図は従来の廃液の処理法を示す流動層式爛焼炉の断
面図、第2図は本発明の処理法を示す燗焼炉の断面図、
第3図falは流動層部とヒータ数句例を示す正面図、
第3図(blは第3図(a)のA−A線断面図、第4図
(alはヒータ取付状況を示す断面図、第4図fblは
第4図falのA−A線断面図である。
・ 1・・爛焼炉、2・・風箱部、3・・流動層部、4
・・フリーボード部、5・・分散板、6・・ヒータ、7
・・外部ヒータ、8・・流動化ガス、9・・流動媒体、
10・・処理廃液、11・・ガス出口、13・・保温材
。
第1図 第2図
第3図
第4図
第1頁の続き
@発明者上島 直幸
@発明者橋本 泰英
高砂市荒井町新浜2丁目1番1号 三菱重工業株式会社
高神戸市兵庫区小松通5丁目1番16号 菱重環境流通
エンジニアリング株式会社内Fig. 1 is a cross-sectional view of a fluidized bed type kiln showing a conventional waste liquid treatment method, and Fig. 2 is a cross-sectional view of a kiln showing a treatment method of the present invention.
Figure 3 fal is a front view showing several examples of the fluidized bed section and the heater;
Figure 3 (bl is a cross-sectional view taken along the line A-A of Figure 3 (a), Figure 4 (al is a cross-sectional view showing the heater installation situation, Figure 4 fbl is a cross-sectional view taken along the line A-A of Figure 4 fal)・ 1. Burning furnace, 2. Wind box section, 3. Fluidized bed section, 4
...Freeboard section, 5.Dispersion plate, 6.Heater, 7
...external heater, 8.. fluidizing gas, 9.. fluidizing medium,
10... Processing waste liquid, 11... Gas outlet, 13... Heat insulation material. Figure 1 Figure 2 Figure 3 Figure 4 Continued from page 1 @ Inventor Naoyuki Uejima @ Inventor Hashimoto Yasue 2-1-1 Shinhama, Arai-cho, Takasago City Mitsubishi Heavy Industries, Ltd. Takako 5-chome, Komatsudori, Hyogo-ku, Kobe City No. 1-16 Inside Ryoju Environmental Distribution Engineering Co., Ltd.
Claims (1)
’.する方法において、前記流動層部壁面を加熱しなが
ら、前記廃液を150℃以上、好ましくは300′゛0
〜350゜Cで流動燻焼することを特徴とする爛焼炉の
廃液処理法。The waste liquid is supplied to the fluidized bed part of the fluidized N smoking furnace and burnt out f! 4
'. In the method of
A method for treating waste liquid from a burning furnace, characterized by fluidized smoldering at ~350°C.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2718684A JPS60174419A (en) | 1984-02-17 | 1984-02-17 | Method of processing waste liquid from calcining furnace |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2718684A JPS60174419A (en) | 1984-02-17 | 1984-02-17 | Method of processing waste liquid from calcining furnace |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS60174419A true JPS60174419A (en) | 1985-09-07 |
Family
ID=12214042
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2718684A Pending JPS60174419A (en) | 1984-02-17 | 1984-02-17 | Method of processing waste liquid from calcining furnace |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS60174419A (en) |
-
1984
- 1984-02-17 JP JP2718684A patent/JPS60174419A/en active Pending
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