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JPH0335578B2 - - Google Patents
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JPH0335578B2 - - Google Patents

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Publication number
JPH0335578B2
JPH0335578B2 JP62018883A JP1888387A JPH0335578B2 JP H0335578 B2 JPH0335578 B2 JP H0335578B2 JP 62018883 A JP62018883 A JP 62018883A JP 1888387 A JP1888387 A JP 1888387A JP H0335578 B2 JPH0335578 B2 JP H0335578B2
Authority
JP
Japan
Prior art keywords
exhaust gas
temperature
wet waste
dry
containing chlorine
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 - Lifetime
Application number
JP62018883A
Other languages
Japanese (ja)
Other versions
JPS63187017A (en
Inventor
Shunji Inoe
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP1888387A priority Critical patent/JPS63187017A/en
Publication of JPS63187017A publication Critical patent/JPS63187017A/en
Publication of JPH0335578B2 publication Critical patent/JPH0335578B2/ja
Granted legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は火力発電所、原子力発電所等の海水取
水口や排水口付近に繁茂あるいは捕集されて、定
期的に除去、回収される海藻のような塩素を含む
湿潤廃棄物の焼却処理方法に関するものである。
Detailed Description of the Invention (Field of Industrial Application) The present invention is applied to seaweed that grows or collects near seawater intakes and drainage ports of thermal power plants, nuclear power plants, etc., and is regularly removed and collected. The present invention relates to a method for incinerating wet waste containing chlorine, such as chlorine-containing wet waste.

(従来の技術) 発電所の海水取水口や排水口付近には多量の海
藻類が繁茂しスクリーン等に捕集されて水の流れ
を妨げるので、定期的に除去し陸上に回収する必
要がある。このように回収された海藻類は従来は
敷地内に埋立てられていたが埋立用地が次第に不
足して来るとともに、腐敗して周囲に悪臭を発す
る欠点がある。また回収された海藻類を焼却炉に
より焼却する試みもなされているが、海水中の塩
素を含有しているため塩化水素ガスが発生し設備
が著しく腐食すること、および燃焼温度が低いた
め未燃カーボンが多量に発生し、フイルタ等の内
部で火災を発生するおそれがあること、異臭が発
生すること等の問題点があつた。
(Conventional technology) A large amount of seaweed grows near the seawater intake and drainage ports of power plants and is collected on screens, etc., obstructing the flow of water, so it is necessary to periodically remove it and collect it on land. . Conventionally, the seaweed collected in this way was buried within the site, but there is a gradual shortage of land for landfill, and the problem is that it rots and gives off a bad odor to the surrounding area. Attempts have also been made to incinerate the collected seaweed in an incinerator, but due to the chlorine in the seawater, hydrogen chloride gas is generated and the equipment is severely corroded, and the combustion temperature is low, resulting in unburned There were problems such as the generation of a large amount of carbon, which could cause a fire inside the filter, etc., and the generation of a strange odor.

(発明が解決しようとする問題点) 本発明は上記のような従来の問題点を解消し
て、焼却による大幅な減容化が可能であり、また
塩化水素による設備の腐食を防止でき、しかも異
臭を発生することもない塩素を含む湿潤廃棄物の
焼却処理方法を目的として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, enables significant volume reduction by incineration, prevents corrosion of equipment due to hydrogen chloride, and This method was developed for the purpose of incinerating wet waste containing chlorine without emitting any strange odors.

(問題点を解決するための手段) 本発明は、塩素を含む湿潤廃棄物を乾燥排ガス
温度が300℃以下である熱風式乾燥機により乾燥
し、乾燥物を乾燥排ガスとともに焼却炉へ導入し
て600℃以上の温度で焼却し焼却灰として取出す
一方、焼却排ガスを耐火物で内張りされた配管に
より直接冷却用空気混合器へ導き、冷却用空気混
合器において冷却用空気を混合して150〜350℃に
冷却したうえ、冷却された焼却排ガスをオーステ
ナイト系ステンレス鋼の配管により導き、必要に
応じて除塵して誘引フアンにより大気中へ放出す
ることを特徴とするものである。
(Means for Solving the Problems) The present invention dries wet waste containing chlorine using a hot air dryer with a dry exhaust gas temperature of 300°C or less, and introduces the dried waste into an incinerator together with the dry exhaust gas. It is incinerated at a temperature of 600℃ or higher and taken out as incineration ash, while the incineration exhaust gas is guided directly to a cooling air mixer through piping lined with refractory material, and the cooling air is mixed in the cooling air mixer to produce a 150 to 350 ℃, the cooled incineration exhaust gas is guided through austenitic stainless steel piping, and if necessary, dust is removed and discharged into the atmosphere using an induction fan.

以下に本発明を図示の実施例とともに詳細に説
明すると、1はロータリー型の熱風式乾燥機、2
は熱風発生炉であつて、海藻類のような塩素を含
む湿潤廃棄物は材料バンカ3からまずこの熱風式
乾燥機1に投入され乾燥される。乾燥条件は乾燥
排ガス温度が300℃以下、望ましくは200℃程度に
維持され、これによつて含水率が約85重量%(以
下重量%にて示す)の湿潤廃棄物は含水率が40%
程度となるまで乾燥されるが、乾燥物の温度は大
半が乾燥排ガスの湿球温度である80℃、水分を全
く含まない部分でも300℃以下であり、折出した
塩(NaCl)はこの温度では分解してHClガスが
発生することはない。次に乾燥品は乾燥品コンベ
ア4により中間ホツパ5を介して焼却炉6へ投入
される。一方、乾燥機の乾燥排ガスは集塵機7に
より除塵されたうえ循環フアン8により一部は熱
風発生炉2へ戻され、他の部分は焼却炉6へ吹込
まれる。焼却炉6には燃焼空気フアン9とバーナ
10とによつて燃焼用空気と高温の燃焼ガスとが
吹込まれ、600℃以上、1000℃以下好ましくは800
℃前後の温度で焼却される。焼却温度を600℃以
上としたのは乾燥時に発生する異臭を完全に分解
して無臭化するためと良好な燃焼をさせ焼却排ガ
ス中の未燃カーボンを低減するためであり、また
1000℃以下としたのは焼却炉6内面の耐火物の損
傷を防止するためである。このようにして焼却炉
6によつて焼却された廃棄物は焼却灰となり、灰
冷却コンベア11により冷却されたうえ灰コンベ
ア12、灰バンカ13を介して外部へ搬出され
る。一方、燃焼により発生した塩酸ガスを含む焼
却排ガスは耐火物で内張りされた配管14によつ
て空気混合器15へ導かれ、冷却用空気が混合さ
れて150〜350℃にまで冷却される。温度が150℃
以下となると塩酸ガスを含有する排ガスは露点に
達して塩酸の結露を生じ、配管に電気化学的腐食
を生じさせる。また温度が350℃以上となると塩
化鉄又はアルカリ鉄硫酸塩等の形成および分解に
よるいわゆる高温腐食が発生する。本発明におい
てはこのため排ガス温度を150〜350℃の範囲、よ
り好ましくは200〜300℃の温度範囲内にコントロ
ールして塩酸ガスによる腐食を防止しており、こ
れ以降の配管をオーステナイト系ステンレス鋼の
ような耐食性に優れた金属の配管とすることがで
きる。このように冷却された焼却排ガスは集塵機
16によつて除塵されたうえ誘引フアン17によ
り誘引され煙突18から大気中に放出される。な
お配管14の途中に塩化水素吸収装置を設けれ
ば、以下の配管の塩酸ガスによる腐食をより確実
に防止することができる。
The present invention will be explained in detail below with reference to illustrated embodiments. 1 is a rotary hot air dryer; 2 is a rotary hot air dryer;
is a hot air generating furnace, and wet waste containing chlorine such as seaweed is first charged into this hot air dryer 1 from a material bunker 3 and dried. The drying conditions are such that the drying exhaust gas temperature is maintained at 300℃ or less, preferably around 200℃, so that wet waste with a moisture content of approximately 85% by weight (hereinafter expressed in weight%) has a moisture content of 40%.
However, the temperature of the dried material is mostly 80℃, which is the wet bulb temperature of the dry exhaust gas, and even the part that does not contain any moisture is below 300℃, and the precipitated salt (NaCl) is dried at this temperature. It will not decompose and produce HCl gas. Next, the dried products are fed into an incinerator 6 via an intermediate hopper 5 by a dry product conveyor 4. On the other hand, the dry exhaust gas from the dryer is removed by a dust collector 7, and then a part is returned to the hot air generating furnace 2 by a circulation fan 8, and the other part is blown into an incinerator 6. Combustion air and high-temperature combustion gas are blown into the incinerator 6 by a combustion air fan 9 and a burner 10 at a temperature of 600°C or higher and 1000°C or lower, preferably 800°C.
It is incinerated at temperatures around ℃. The reason why the incineration temperature was set at 600℃ or higher was to completely decompose the odor generated during drying and make it odorless, and also to ensure good combustion and reduce unburned carbon in the incineration exhaust gas.
The reason for setting the temperature to 1000°C or lower is to prevent damage to the refractories on the inner surface of the incinerator 6. The waste thus incinerated in the incinerator 6 becomes incinerated ash, which is cooled by an ash cooling conveyor 11 and then transported to the outside via an ash conveyor 12 and an ash bunker 13. On the other hand, incineration exhaust gas containing hydrochloric acid gas generated by combustion is led to an air mixer 15 through a pipe 14 lined with a refractory material, where it is mixed with cooling air and cooled to 150 to 350°C. temperature is 150℃
Below this, the exhaust gas containing hydrochloric acid gas will reach the dew point and cause hydrochloric acid condensation, causing electrochemical corrosion in the piping. Furthermore, when the temperature exceeds 350°C, so-called high-temperature corrosion occurs due to the formation and decomposition of iron chloride or alkali iron sulfate. Therefore, in the present invention, the exhaust gas temperature is controlled within the range of 150 to 350℃, more preferably within the temperature range of 200 to 300℃ to prevent corrosion caused by hydrochloric acid gas, and the piping after this is made of austenitic stainless steel. It is possible to use metal piping with excellent corrosion resistance, such as The incineration exhaust gas cooled in this manner is removed by a dust collector 16, drawn by an induction fan 17, and discharged into the atmosphere from a chimney 18. Note that if a hydrogen chloride absorption device is provided in the middle of the piping 14, corrosion of the piping described below due to hydrochloric acid gas can be more reliably prevented.

以上に説明した設備により、含水率85%の海藻
を排ガス出口温度が200℃の熱風式乾燥機1に280
Kg/Hrの割合で供給し、含水率40%の乾燥物を
70Kg/Hrの割合で得たが乾燥排ガス中に塩化水
素は検出されなかつた。このような乾燥物を炉内
温度が800℃に保たれた焼却炉6に投入したとこ
ろ焼却灰の発生量は10Kg/Hrであり、重量減少
比は280/10の28倍であつた。またこのときの焼
却排ガス中の塩化水素ガス濃度は50〜100ppmで
あつたが、空気混合器15により300℃まで冷却
したところ、以後の配管中に腐食は全く認められ
ず、また煙突18から放出された排ガス中の異臭
は全く検知されなかつた。
With the equipment explained above, seaweed with a moisture content of 85% is transferred to hot air dryer 1 with an exhaust gas outlet temperature of 200°C.
Supplied at a ratio of Kg/Hr, dry matter with a moisture content of 40% is supplied.
Although it was obtained at a rate of 70Kg/Hr, no hydrogen chloride was detected in the dry exhaust gas. When such dried material was put into the incinerator 6 whose internal temperature was maintained at 800°C, the amount of incinerated ash generated was 10 kg/Hr, and the weight reduction ratio was 28 times of 280/10. In addition, the concentration of hydrogen chloride gas in the incineration exhaust gas at this time was 50 to 100 ppm, but when it was cooled to 300 degrees Celsius using the air mixer 15, no corrosion was observed in the subsequent piping, and it was released from the chimney 18. No abnormal odor was detected in the exhaust gas.

(発明の効果) 本発明は以上の説明からも明らかなように、海
藻のような塩素を含む湿潤廃棄物を焼却すること
により大幅な減容化が可能であり、従来のような
埋立用地の不足を解消することができる。また本
発明によれば600℃以上の高温度で焼却が行われ
るので悪臭および多量の未燃カーボンが発生する
こともなく、更に焼却排ガスは塩化水素ガスによ
る露点腐食や高温腐食を生ずるおそれのない150
〜350℃の温度にまで冷却されるので設備の腐食
を防止することができる。よつて本発明は特に火
力発電所や原子力発電所の海水取水口や排水口に
繁茂あるいは捕集される海藻類の焼却に好適な塩
素を含む湿潤廃棄物の焼却処理方法として、産業
の発展に寄与するところは極めて大である。
(Effects of the Invention) As is clear from the above explanation, the present invention can significantly reduce the volume of wet waste containing chlorine such as seaweed by incinerating it, making it possible to significantly reduce the volume of wet waste that contains chlorine, such as seaweed. The shortage can be resolved. Furthermore, according to the present invention, incineration is carried out at a high temperature of 600°C or higher, so there is no foul odor or large amount of unburned carbon, and the incineration exhaust gas is free from the risk of dew point corrosion or high temperature corrosion caused by hydrogen chloride gas. 150
Since it is cooled to a temperature of ~350°C, corrosion of equipment can be prevented. Therefore, the present invention is particularly useful for the development of industry as a method for incinerating wet waste containing chlorine, which is suitable for incinerating seaweed that grows or is collected in seawater intakes and drains of thermal power plants and nuclear power plants. The contribution made is extremely large.

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

第1図は本発明の工程の一実施例を示すフロー
シートである。 1:熱風式乾燥機、6:焼却炉、15:空気混
合器。
FIG. 1 is a flow sheet showing one embodiment of the process of the present invention. 1: Hot air dryer, 6: Incinerator, 15: Air mixer.

Claims (1)

【特許請求の範囲】 1 塩素を含む湿潤廃棄物を乾燥排ガス温度が
300℃以下である熱風式乾燥機により乾燥し、乾
燥物を乾燥排ガスとともに焼却炉へ導入して600
℃以上の温度で焼却し焼却灰として取出す一方、
焼却排ガスを耐火物で内張りされた配管により直
接冷却用空気混合器へ導き、冷却用空気混合器に
おいて冷却用空気を混合して150〜350℃に冷却し
たうえ、冷却された焼却排ガスをオーステナイト
系ステンレス鋼の配管により導き、必要に応じて
除塵して誘引フアンにより大気中へ放出すること
を特徴とする塩素を含む湿潤廃棄物の焼却処理方
法。 2 焼却炉の焼却温度が600〜1000℃である特許
請求の範囲第1項記載の塩素を含む湿潤廃棄物の
焼却処理方法。 3 熱風式乾燥機の乾燥排ガスの一部を乾燥機の
熱風発生炉へ循環使用するようにした特許請求の
範囲第1項記載の塩素を含む湿潤廃棄物の焼却処
理方法。
[Claims] 1. Dry wet waste containing chlorine when the exhaust gas temperature is
Dry in a hot air dryer with a temperature of 300℃ or less, and introduce the dried material into an incinerator together with dry exhaust gas for 600℃.
While it is incinerated at temperatures above ℃ and taken out as incineration ash,
The incineration exhaust gas is guided directly to the cooling air mixer through a pipe lined with refractory material, and the cooling air is mixed in the cooling air mixer and cooled to 150 to 350℃. A method for incinerating wet waste containing chlorine, which is guided through stainless steel piping, removed as necessary, and discharged into the atmosphere using an induction fan. 2. The method for incinerating wet waste containing chlorine according to claim 1, wherein the incinerator has an incineration temperature of 600 to 1000°C. 3. A method for incinerating wet waste containing chlorine according to claim 1, wherein a part of the dry exhaust gas from the hot air dryer is recycled to the hot air generating furnace of the dryer.
JP1888387A 1987-01-29 1987-01-29 Incineration treating method for wet waste containing chlorine Granted JPS63187017A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1888387A JPS63187017A (en) 1987-01-29 1987-01-29 Incineration treating method for wet waste containing chlorine

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1888387A JPS63187017A (en) 1987-01-29 1987-01-29 Incineration treating method for wet waste containing chlorine

Publications (2)

Publication Number Publication Date
JPS63187017A JPS63187017A (en) 1988-08-02
JPH0335578B2 true JPH0335578B2 (en) 1991-05-28

Family

ID=11983956

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1888387A Granted JPS63187017A (en) 1987-01-29 1987-01-29 Incineration treating method for wet waste containing chlorine

Country Status (1)

Country Link
JP (1) JPS63187017A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB9317157D0 (en) * 1993-08-18 1993-10-20 Foss Rupert N M Machines powered by secret fuel
JP2006308173A (en) * 2005-04-27 2006-11-09 Takasago Ind Co Ltd Batch rotary kiln
WO2007085618A1 (en) * 2006-01-25 2007-08-02 Nv Bekaert Sa Convective system for a dryer installation
CN102607041B (en) * 2012-03-23 2014-08-13 上海康恒环境股份有限公司 Sludge pretreatment device for house refuse and municipal sludge fixed burning

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS54139878A (en) * 1978-04-24 1979-10-30 Nippon Kokan Kk <Nkk> Treating method for carbage incinerator exhaust gas
JPS54149272A (en) * 1978-05-15 1979-11-22 Babcock Hitachi Kk Incinerator device
JPS54149274A (en) * 1978-05-15 1979-11-22 Babcock Hitachi Kk Incinerator device
JPS5594696A (en) * 1979-01-10 1980-07-18 Okawara Mfg Co Ltd Device for jointly drying and incinerating sludge or the like
JPS5719011A (en) * 1980-07-04 1982-02-01 Mitsubishi Heavy Ind Ltd Dusting apparatus for waste gas of incineration of heavy oil ash
JPS5912733A (en) * 1982-07-13 1984-01-23 Hitachi Zosen Corp Removal of harmful gas in drying system of organic waste material

Also Published As

Publication number Publication date
JPS63187017A (en) 1988-08-02

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