JP2997989B2 - Method for treating incineration residue discharged from marine incinerator using slurry filter - Google Patents

Method for treating incineration residue discharged from marine incinerator using slurry filter

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Publication number
JP2997989B2
JP2997989B2 JP28450294A JP28450294A JP2997989B2 JP 2997989 B2 JP2997989 B2 JP 2997989B2 JP 28450294 A JP28450294 A JP 28450294A JP 28450294 A JP28450294 A JP 28450294A JP 2997989 B2 JP2997989 B2 JP 2997989B2
Authority
JP
Japan
Prior art keywords
water
incineration
incineration residue
residue
tank
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.)
Expired - Fee Related
Application number
JP28450294A
Other languages
Japanese (ja)
Other versions
JPH08119690A (en
Inventor
清 清水
清爾 渡
哲夫 石川
重 御手洗
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.)
Nippon Steel Corp
Nippon Steel Plant Designing Corp
Original Assignee
Nittetsu Plant Designing Corp
Nippon Steel Corp
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Application filed by Nittetsu Plant Designing Corp, Nippon Steel Corp filed Critical Nittetsu Plant Designing Corp
Priority to JP28450294A priority Critical patent/JP2997989B2/en
Publication of JPH08119690A publication Critical patent/JPH08119690A/en
Application granted granted Critical
Publication of JP2997989B2 publication Critical patent/JP2997989B2/en
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Expired - Fee Related legal-status Critical Current

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Description

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

【0001】[0001]

【産業上の利用分野】本発明は、各種工場,発電所など
の冷却用海水路に付着した貝,食用貝肉又は真珠採取後
の貝殻などを処理する海生物焼却炉から排出される焼却
残渣の処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an incineration residue discharged from a marine incinerator for treating shells, edible shell meat or shells after collecting pearls, etc. attached to cooling sea waterways of various factories and power plants. Regarding the processing method.

【0002】[0002]

【従来の技術】発電所,製鉄プラントまたは化学プラン
ト等において、冷却水として海水が用いられる場合が多
い。海水を冷却水しとて使用する場合、その水路(管
路)に貝類等海生物が付着・成長する結果、必要水量が
確保できなくなるため、定期的にこれら海生物を除去す
る必要がある。
2. Description of the Related Art Seawater is often used as cooling water in power plants, steelmaking plants, chemical plants, and the like. When seawater is used as cooling water, seawater such as shellfish adheres to and grows in the waterway (pipeline), and as a result, the required amount of water cannot be secured. Therefore, it is necessary to periodically remove these seawater.

【0003】これら貝殻などを含む海生物は、通常ロー
タリーキルン等の焼却炉で焼却されている。この焼却処
理方法を行うことにより主成分である炭酸カルシウム
(CaCO3 )は、下記(1)式に示す反応により、生
石灰(CaO)になる。更に水を加えることにより、
(2)式に示す消化反応により消石灰〔Ca(O
H)2 〕となる。
[0003] Marine organisms including these shells are usually incinerated in an incinerator such as a rotary kiln. By performing this incineration method, calcium carbonate (CaCO 3 ) as a main component is converted into quick lime (CaO) by a reaction represented by the following formula (1). By adding more water,
Slaked lime [Ca (O
H) 2 ].

【0004】[0004]

【数1】 CaCO3 =CaO+CO2 −42.9kcal/mol ……(1)## EQU1 ## CaCO 3 = CaO + CO 2 -42.9 kcal / mol (1)

【0005】[0005]

【数2】 CaO+H2 O=Ca(OH)2 +15.2kcal/mol ……(2)## EQU2 ## CaO + H 2 O = Ca (OH) 2 +15.2 kcal / mol (2)

【0006】(1)式の反応により生成した焼却残渣で
ある生石灰を、運搬及び埋立等の処理に適した消石灰に
するため、(2)式の消化反応を行い生石灰を消石灰に
する必要がある。この方法として、乾式法及び湿式法が
知られている。
[0006] In order to convert quicklime, which is an incineration residue generated by the reaction of the formula (1), into slaked lime suitable for processing such as transportation and landfill, it is necessary to convert the quicklime into slaked lime by performing a digestion reaction of the formula (2). . As this method, a dry method and a wet method are known.

【0007】乾式法では、焼却残渣である生石灰をスク
リューコンベアやフライトコンベア等で焼却炉から搬送
した後、消化,冷却及び加湿に必要な水量を専用のナウ
ターミキサー等の消化槽にて散水し、消化,冷却及び加
湿を行う。この時、消化反応で生じる消石灰の微細な粉
末や消化反応による発熱にて生じる水蒸気は、ブロワに
より吸引し、バグフィルター等で除塵している。
[0007] In the dry method, quicklime, which is an incineration residue, is transported from an incinerator by a screw conveyor, a flight conveyor, or the like, and then water required for digestion, cooling, and humidification is sprinkled in a digestion tank such as a special Nauta mixer. Perform digestion, cooling and humidification. At this time, the fine powder of slaked lime generated by the digestion reaction and the water vapor generated by the heat generated by the digestion reaction are sucked by a blower and removed by a bag filter or the like.

【0008】一方湿式法は、例えば特開平4−9350
8号公報に開示されているように、焼却残渣を水槽に浸
漬させ、スクレーパーで掻き揚げる方法が行われてい
る。また特開平6−72745号公報には、水槽に浸漬
される焼却残渣の浸漬時間を制御することにより、H2
O/CaO反応当量比を0.7未満とする結果、浸漬後
の焼却残渣の残留付着水を低減することが開示されてい
る。
On the other hand, the wet method is disclosed in, for example,
As disclosed in Japanese Patent Application Publication No. 8 (1999), a method is used in which the incineration residue is immersed in a water tank and scraped up with a scraper. JP-A-6-72745 discloses that the immersion time of incineration residues immersed in a water tank is controlled so that H 2
It is disclosed that as a result of making the O / CaO reaction equivalent ratio less than 0.7, the amount of residual water adhering to the incineration residue after immersion is reduced.

【0009】[0009]

【発明が解決しようとする課題】前記乾式法の場合は、
添加する水が生石灰との発熱反応により突沸するため、
生成した消石灰の微細な粉末を巻き上げると共に水蒸気
をともない、排気ダクト及び集塵用バグフィルターに付
着しこれを閉塞させ、安定運転や自動運転を阻害してい
る。
In the case of the dry method,
Because the water to be added is bumped by the exothermic reaction with quicklime,
The fine powder of slaked lime produced is rolled up and accompanied by water vapor, adheres to the exhaust duct and the bag filter for dust collection and closes it, thereby hindering stable operation and automatic operation.

【0010】前記湿式法では、水槽に浸漬させるために
水槽で生成した消石灰の微細な粉末がスラリーとして濃
縮されるために、掻き揚げた消石灰にスラリーが同伴
し、含有水分が多くなる。この結果、輸送途中での分離
したスラリーのこぼれや搬送機器へのスラッジ付着及び
固着が生じる。
In the above-mentioned wet method, fine powder of slaked lime generated in the water tank to be immersed in the water tank is concentrated as a slurry, so that the slurry accompanies the scoured slaked lime and the water content increases. As a result, spilling of the separated slurry during transportation and adhesion and fixation of sludge to the transport equipment occur.

【0011】またホッパー内でもスラッジ付着による閉
塞が起こり、更にホッパーからの焼却残渣排出物の輸送
の際にも、公道上にスラリーがこぼれる等、環境を阻害
する問題があった。
Also, there is a problem in that the environment is hindered, such as clogging due to sludge adhesion in the hopper, and furthermore, when transporting incineration residue discharged from the hopper, slurry is spilled on public roads.

【0012】前記特開平6−72745号公報の技術で
は、水封槽での消化反応をH2 O/CaO反応当量比
0.7未満とすることにより、焼却残渣の残留付着水分
を30%以下にすることが示されている。この方法は、
コンベアの搬送スピード及び水封槽内水中搬送距離を調
節することにより目的を達成することが可能であるが、
その制御が難しいという問題を有している。
In the technique disclosed in Japanese Patent Laid-Open No. Hei 6-72745, the digestion reaction in a water-sealed tank is set to an H 2 O / CaO reaction equivalent ratio of less than 0.7, so that the residual moisture adhering to the incineration residue is reduced to 30% or less. It is shown that This method
It is possible to achieve the purpose by adjusting the conveyor speed and the water transfer distance in the water seal tank,
There is a problem that the control is difficult.

【0013】本発明は上記課題に鑑み、簡易な設備で取
扱に適した水分を有する海生物焼却残渣を、容易に安定
して生産する焼却残渣の処理方法を提供する。
The present invention has been made in view of the above problems, and provides a method for treating incineration residues that easily and stably produces marine incineration residues having water suitable for handling with simple equipment.

【0014】[0014]

【課題を解決するための手段】上記問題を解決する本発
明は、焼却炉の焼却残渣排出口の下部に焼却残渣排出コ
ンベア付の水封槽を設置した海生物焼却処理装置を使用
した焼却残渣の処理方法において、消化反応により水封
槽内に生成する微細なスラリー状の消石灰粉末を水封槽
の中段から抜き取り、これを遠心分離機又は濾過式分離
機で水分と固形物に分離し、他方水封槽内に残る粗粒残
渣はスクレーパー付きコンベアにより搬送して前記分離
した固形物と混合させることを特徴とするスラリー濾過
器を用いた海生物焼却炉から排出される焼却残渣の処理
方法である。
According to the present invention, there is provided an incineration residue using a marine incineration apparatus having a water ring tank provided with an incineration residue discharge conveyor below an incineration residue discharge port of an incinerator. In the treatment method, the fine slurry-like slaked lime powder generated in the water seal tank by the digestion reaction is withdrawn from the middle stage of the water seal tank, and separated into water and solids by a centrifuge or a filtration separator, On the other hand, a method for treating incineration residues discharged from a marine incinerator using a slurry filter, wherein the coarse residue remaining in the water seal tank is conveyed by a conveyor with a scraper and mixed with the separated solid matter. It is.

【0015】[0015]

【作用】即ち本発明は、水封槽内の消化反応により生成
した微細なスラリー状の消石灰粉末を水封槽の中段から
抜き出し、遠心分離機又は濾過式分離機により除去して
水分の減少した消石灰粉末はホッパーへ、また分離水は
水封槽へ戻す。
According to the present invention, fine slurry-like slaked lime powder produced by the digestion reaction in the water-sealed tank is extracted from the middle stage of the water-sealed tank and removed by a centrifugal separator or a filtration separator to reduce water content. The slaked lime powder is returned to the hopper, and the separated water is returned to the water seal tank.

【0016】他方、水封槽の底部から掻き上げられた粗
粒の焼却残渣は、水切れがよくスラリー分を同伴しない
為、付着水分が減少した状態で上記ホッパーへ搬送さ
れ、分離された固形物と混合される。この得られた混合
焼却残渣の付着水分は20〜30%で、残渣取扱いが容
易である。
On the other hand, the incineration residue of coarse particles scooped up from the bottom of the water-sealed tank is often drained and does not accompany the slurry, so that it is conveyed to the above-mentioned hopper in a state where the attached moisture is reduced, and the separated solid matter is separated. Mixed with. The moisture content of the obtained mixed incineration residue is 20 to 30%, and the handling of the residue is easy.

【0017】貝殻を含む海生物は、ロータリーキルン等
により、排ガス温度が約700〜850℃で焼却され、
焼却残渣は焼却炉の下部に設けたスクレーパー付水封槽
に入る。水封槽では消化反応により生成した微細な消石
灰粉末を含むスラリーが生じる。このスラリー量は焼却
残渣処理量の増加と共に増加し、スラリー濃度も増加し
てついには水封槽の機能不良に陥る。この為、このスラ
リーを水封槽中段から抜き出して遠心分離機や濾過式分
離機により固液分離する。水分の減少した固形物はホッ
パーへ貯留し、分離水は水封槽へ戻す。
[0017] Sea life including shells is incinerated by a rotary kiln or the like at an exhaust gas temperature of about 700 to 850 ° C.
The incineration residue enters a water seal tank with a scraper provided in the lower part of the incinerator. In the water seal tank, a slurry containing fine slaked lime powder generated by the digestion reaction is generated. This amount of slurry increases with an increase in the amount of incineration residue treated, and the slurry concentration also increases, eventually leading to malfunction of the water seal tank. For this reason, this slurry is extracted from the middle stage of the water-sealed tank and solid-liquid separated by a centrifugal separator or a filtration type separator. The solid with reduced moisture is stored in a hopper, and the separated water is returned to a water seal tank.

【0018】一方水封槽では、スラリーが除去される結
果粗粒の焼却残渣が残る。この残渣は粗粒であるため水
切れがよく、スクレーパーで掻き上げた残渣の付着水に
ついても減少する。残渣の搬送の際にもスラリーのこぼ
れや搬送機器への付着が無くなり、ホッパーへ搬送され
て上述の遠心分離機分離固形物と混合貯留される。この
ような過程を経て、ホッパーへ混合貯留された焼却残渣
の付着水は20〜30%で取扱いが容易な残渣が得られ
る。
On the other hand, in the water-sealed tank, coarse incineration residues remain as a result of removal of the slurry. Since the residue is coarse, the drainage is good and the amount of water adhering to the residue scraped up by the scraper is reduced. When the residue is transported, the slurry does not spill or adhere to the transport device, and is transported to the hopper to be mixed and stored with the above-mentioned centrifugal separator separated solid. Through such a process, the amount of water adhering to the incineration residue mixed and stored in the hopper is 20 to 30%, and a residue that can be easily handled is obtained.

【0019】本願発明者らは、予備テストとしてホッパ
ーへ貯留される混合焼却残渣の付着水を調査した結果、
20〜30%であることが判明した。この水分量は、2
0%以下では発塵性が増加し、30%以上では流動性が
増加するため、焼却残渣の取扱いには最適な水分量であ
ることが分かった。
As a preliminary test, the inventors of the present application have investigated the adhering water of the mixed incineration residue stored in the hopper.
It turned out to be 20-30%. This water content is 2
When the content is 0% or less, the dusting property increases, and when the content is 30% or more, the fluidity increases.

【0020】[0020]

【実施例】以下図1に示す実施例に従って、本発明を説
明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below with reference to the embodiment shown in FIG.

【0021】図1は、海生物の焼却,消化処理装置の一
例を示し、発電所の冷却用海水路等に付着した泥を含む
貝を、装入ホッパー1から装入スクリュコンベア2によ
りロータリーキルン4に投入し、ロータリーキルン4内
ではバーナー3の燃焼排ガスにより約700〜850℃
の温度で焼却し、この焼却残渣を炉尻フード6下部の焼
却残渣落口ダクト8より水封槽7内に落下,投入した。
FIG. 1 shows an example of an apparatus for incinerating and digesting marine organisms. A shell containing mud adhering to a cooling seawater channel or the like of a power plant is rotated from a charging hopper 1 to a rotary kiln 4 by a charging screw conveyor 2. And in the rotary kiln 4, about 700 to 850 ° C. due to the combustion exhaust gas of the burner 3.
The incineration residue was dropped from the incineration residue outlet duct 8 at the bottom of the furnace hood 6 into the water-sealed tank 7.

【0022】次いで水封槽7の消化反応により生じる消
石灰スラリーを、水封槽7中段からスラリー移送ポンプ
12により選択的に抽出し、これを遠心分離機13に装
入して、その残渣はホッパー11へ投入し、分離水は水
封槽7へ逆送した。本実施例では、この分離を遠心分離
機で説明したが、濾過式分離機を使用してもよい。
Next, slaked lime slurry generated by the digestion reaction of the water sealing tank 7 is selectively extracted from the middle stage of the water sealing tank 7 by the slurry transfer pump 12 and charged into the centrifugal separator 13. 11 and the separated water was sent back to the water seal tank 7. In this embodiment, this separation is described using a centrifuge, but a filtration type separator may be used.

【0023】水封槽7内に残る粗粒残渣は、スクレーパ
ー付コンベア14により掻き出され、焼却灰移送コンベ
ア10によりホッパー11へ搬送した。搬送途中ではス
ラリーのこぼれもなく、搬送機器への付着も少ないこと
を確認した。更にホッパー11へ貯留した混合焼却残渣
は、取扱い性が良いことも確認すると共に、付着水分に
ついても20〜30%であることが判った。
The coarse-grained residue remaining in the water sealing tank 7 was scraped out by a conveyor 14 with a scraper, and was conveyed to a hopper 11 by an incineration ash transfer conveyor 10. It was confirmed that there was no spilling of the slurry during the transportation and that the adhesion to the transportation equipment was small. Further, the mixed incineration residue stored in the hopper 11 was confirmed to have good handleability, and it was also found that the amount of adhering moisture was 20 to 30%.

【0024】[0024]

【発明の効果】以上説明したように本発明による海生物
焼却残渣の消化方法は、貝殻の様な性状の安定しない海
生物の処理において、従来の湿式法の有する分離したス
ラリーの搬送時の課題、コンベア搬送スピード等の制御
の困難さ等の問題を解決し、消化反応により水封槽内に
生成する消石灰粉末を水封槽から抜き取って水分と固形
物に分離し、これを粗粒残渣と混合させることにより、
残渣の付着水を取扱に適した20〜30%に維持するこ
とができ、従って消化処理装置も従来に比し非常に簡易
となり、取扱い及び運搬に適した含水率を有する焼却残
渣を容易かつ安定して生産することが出来る。
As described above, the method for digesting incineration residues of marine organisms according to the present invention has a problem in transporting separated slurries, which is a conventional wet method, in treating marine organisms having unstable properties such as shells. Solve the problems such as difficulty in controlling the conveyor conveyance speed, etc., remove the slaked lime powder generated in the water seal tank by the digestion reaction from the water seal tank, separate it into moisture and solids, and By mixing
The water adhering to the residue can be maintained at 20 to 30% suitable for handling, so the digestion treatment apparatus is also very simple compared to the conventional one, and the incineration residue having a water content suitable for handling and transport can be easily and stably obtained. Can be produced.

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

【図1】本発明の残渣消化処理を行うに好適な海生物の
焼却,消化処理装置の一例を示す略側面図である。
FIG. 1 is a schematic side view showing an example of a marine incineration and digestion treatment apparatus suitable for performing the residue digestion treatment of the present invention.

【符号の説明】[Explanation of symbols]

1 海生物装入ホッパー 2 海生物装入スクリューコンベア 3 バーナー 4 ロータリーキルン 5 焼却排ガス 6 炉尻フード 7 水封槽 8 焼却残渣落口ダクト 9 焼却残渣 10 焼却灰移送コンベア 11 焼却灰ホッパー 12 スラリー移送ポンプ 13 遠心分離機 14 スクレーパー付コンベア DESCRIPTION OF SYMBOLS 1 Sea life loading hopper 2 Sea life loading screw conveyor 3 Burner 4 Rotary kiln 5 Incineration gas 6 Furnace bottom hood 7 Water seal tank 8 Incineration residue outlet duct 9 Incineration residue 10 Incineration ash transfer conveyor 11 Incineration ash hopper 12 Slurry transfer pump 13 Centrifuge 14 Conveyor with scraper

フロントページの続き (72)発明者 石川 哲夫 北九州市戸畑区大字中原46−59 日鐵プ ラント設計株式会社内 (72)発明者 御手洗 重 北九州市戸畑区大字中原46−59 日鐵プ ラント設計株式会社内 (58)調査した分野(Int.Cl.7,DB名) C04B 2/04 C04B 2/08 F23G 5/00 F23J 1/00 Continuing from the front page (72) Inventor Tetsuo Ishikawa 46-59, Ohara Nakahara, Tobata-ku, Kitakyushu Nippon Steel Plant Design Co., Ltd. (72) Inventor Shigeru Mitarai 46-59, Ohara Nakahara, Tobata-ku, Kitakyushu Nippon Steel Plant Design Stock In-company (58) Field surveyed (Int.Cl. 7 , DB name) C04B 2/04 C04B 2/08 F23G 5/00 F23J 1/00

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 焼却炉の焼却残渣排出口の下部に焼却残
渣排出コンベア付の水封槽を設置した海生物焼却処理装
置を使用した焼却残渣の処理方法において、消化反応に
より水封槽内に生成する微細な消石灰粉末を水封槽の中
段から抜き取り、これを遠心分離機又は濾過式分離機で
水分と固形物に分離し、他方水封槽内に残る粗粒残渣は
スクレーパー付きコンベアにより搬送して前記分離した
固形物と混合させることを特徴とするスラリー濾過器を
用いた海生物焼却炉から排出される焼却残渣の処理方
法。
1. A method for treating incineration residues using a marine incineration treatment apparatus having a water ring tank provided with an incineration residue discharge conveyor below the incineration residue discharge port of an incinerator, wherein the digestion reaction causes the incineration residue to enter the water ring tank. The resulting fine slaked lime powder is extracted from the middle stage of the water-sealed tank and separated into water and solids by a centrifuge or a filtration separator, while the coarse-grained residue remaining in the water-sealed tank is transported by a conveyor with a scraper. And treating the incineration residue discharged from a marine incinerator using a slurry filter.
JP28450294A 1994-10-26 1994-10-26 Method for treating incineration residue discharged from marine incinerator using slurry filter Expired - Fee Related JP2997989B2 (en)

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JP28450294A JP2997989B2 (en) 1994-10-26 1994-10-26 Method for treating incineration residue discharged from marine incinerator using slurry filter

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JP28450294A JP2997989B2 (en) 1994-10-26 1994-10-26 Method for treating incineration residue discharged from marine incinerator using slurry filter

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CN113295568A (en) * 2021-07-12 2021-08-24 河南科技大学 Lime raw burning rate detection device
CN114839988B (en) * 2022-04-28 2023-05-26 哈尔滨工业大学 Protective tail cover separation time sequence control method during high-speed water entry of navigation body

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