JPS61276617A - Burning of phosphorus-containing substance - Google Patents

Burning of phosphorus-containing substance

Info

Publication number
JPS61276617A
JPS61276617A JP11548285A JP11548285A JPS61276617A JP S61276617 A JPS61276617 A JP S61276617A JP 11548285 A JP11548285 A JP 11548285A JP 11548285 A JP11548285 A JP 11548285A JP S61276617 A JPS61276617 A JP S61276617A
Authority
JP
Japan
Prior art keywords
phosphorus
sludge
fluidized bed
burning
ash
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
Application number
JP11548285A
Other languages
Japanese (ja)
Other versions
JPH0523330B2 (en
Inventor
Hiromichi Fujiwara
弘道 藤原
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP11548285A priority Critical patent/JPS61276617A/en
Publication of JPS61276617A publication Critical patent/JPS61276617A/en
Publication of JPH0523330B2 publication Critical patent/JPH0523330B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To obtain a method of burning and treating sludges containing great amounts of phosphorus by adding a calcium compound to the phosphorus- containing substances until at least burning time. CONSTITUTION:In a fluidized bed incinerator, sludges 1 containing great amounts of phosphorus are mixed with a calcium compound 3, e.g., calcium carbonate, etc., in a mixer 2 set on the former stage of the incinerator and then charged into a fluidized bed furnace 4. The sludge 5 is crushed by the fluidizing movement of a fluidizing fluid 6 in the internal lower side of the incinerator, dried, and burned at high temperatures above 600 deg.C. When the heat quantity of the sludge is low, an auxiliary fuel 7 is used in the burning. Phosphoric acid compounds are changed into calcium phosphate and are allowed to incinerate without lowering of the melting point of the ash of the sludge and also any increase in the adhering amount of the ash. The incinerating treatment of the sludges can thus be stably attained without the adherence of the fluidizing mediums, occurrence of clinker, and the adherence of the ash to waste gas processing installation 9.

Description

【発明の詳細な説明】 〈産業上[有]利用分野〉 本発明は流動層を用いた燃焼方法に係り、特にリン含有
量の多い焼却物についても良好な燃焼を行うことのでき
る燃焼方法に関する。
[Detailed description of the invention] <Industrial field of application> The present invention relates to a combustion method using a fluidized bed, and in particular to a combustion method that can perform good combustion even for incinerated materials with a high phosphorus content. .

〈従来の技術及びその問題点〉 下水及び産業排水スラッジの焼却処理に対しては焼却性
能が優秀である点より、流動層式焼却炉の採用が多くな
ってきている。流動層式焼却炉は炉内に保有する流動媒
体の流動化運動により、泥状でかつ塊状の含水スラッジ
を解砕。
<Prior art and its problems> Fluidized bed incinerators are increasingly being used for the incineration treatment of sewage and industrial wastewater sludge due to their excellent incineration performance. Fluidized bed incinerators break up muddy and clumpy water-containing sludge through the fluidization movement of the fluidized medium inside the furnace.

乾燥しかつ燃焼させる。その乾燥及び燃焼効率並びに燃
焼の安定性は全て流動媒体の活発な流動化運動のいかん
にかかつている。通常、流動媒体としては、脱硫、脱塩
化水素というガス処理が不要な場合は、5iOzを主成
分とする川砂あるいは珪砂が使用されている。
Dry and burn. The drying and combustion efficiency as well as the combustion stability all depend on the active fluidizing movement of the fluidizing medium. Usually, river sand or silica sand containing 5 iOz as a main component is used as the fluid medium when gas treatments such as desulfurization and dehydrochlorination are not required.

しかしスラッジの組成によっては、上記した活発な流動
化の維持が困難になる場合がある。
However, depending on the composition of the sludge, it may be difficult to maintain the above-mentioned active fluidization.

例えば食品工業排水の処理等で発生するリン成分を多量
に含むスラッジ焼却に関しては、流動層炉で焼却するに
際しては次のような問題点があった。
For example, when incinerating sludge containing a large amount of phosphorus components generated in the treatment of food industry wastewater, etc., there are the following problems when incinerating it in a fluidized bed furnace.

(1)  スラッジに含まれるリン化合物(P化合物)
は、炉内の高温雰囲気において、ピロ、トリテ。
(1) Phosphorus compounds (P compounds) contained in sludge
In the high-temperature atmosphere inside the furnace, pyro and trite occur.

トラペンタという形で順次脱水縮合する。このような縮
合リン酸に変化すると、粘性が増大し、その結果スラッ
ジ灰分の付着性が高まり、媒体相互間の付着や排ガスに
同伴されるフライアッシュの炉壁あるいは後絞のガス処
理設備への付着が発生する。
It is sequentially dehydrated and condensed in the form of trapenta. When converted to such condensed phosphoric acid, the viscosity increases, resulting in increased adhesion of sludge ash, resulting in adhesion between media and fly ash entrained in exhaust gas to the furnace wall or post-throttling gas treatment equipment. Adhesion occurs.

(2)焼却に際して、上記したリン化合物と流動媒体中
の8102とが約600℃以上の高温下で反応し、リン
酸ガラスを形成させ、その結果媒体が共融し、ガラス状
のタリンカを生成させ、流動化が不可能となる。
(2) During incineration, the above-mentioned phosphorus compound and 8102 in the fluid medium react at high temperatures of approximately 600°C or higher to form phosphate glass, and as a result, the medium undergoes eutectic melting to produce glassy talinka. liquidation becomes impossible.

く本発明の目的〉 本発明の目的は上記した従来技術の欠点をなくシ、媒体
のタリン力トラブル等の問題を発生させることなく、リ
ン含有量の多いスラッジを焼却処理する方法を提供する
ものである。
OBJECTS OF THE INVENTION An object of the present invention is to eliminate the drawbacks of the above-mentioned prior art and provide a method for incinerating sludge with a high phosphorus content without causing problems such as problems with the talin force of the medium. It is.

く本発明の概要〉 第1図に本発明の実施例のフローを示す。Summary of the present invention> FIG. 1 shows the flow of an embodiment of the present invention.

具体的に説明すると、リン含有量の多いスラッジ1は、
炉前段に設置された混練機2で炭酸カルシウム等のカル
シウム化合物3を添加、混練し、しかる後、流動層炉4
へ投入される。投入された混練スラッジ5は、炉内下部
の流動媒体6の流動化運動により、解砕、乾燥され、6
00℃以上の高温下で燃焼する。スラッジの発熱量が低
い場合は、燃焼に際して補助燃料7が使用される。本発
明例において、流動媒体6を含む流動層内では下記(1
) (2)のような反応が生じる。
To explain specifically, sludge 1 with a high phosphorus content is
Calcium compounds 3 such as calcium carbonate are added and kneaded in a kneader 2 installed in the front stage of the furnace, and then transferred to a fluidized bed furnace 4.
will be put into. The introduced kneaded sludge 5 is crushed and dried by the fluidization movement of the fluidized medium 6 in the lower part of the furnace.
Burns at high temperatures above 00℃. If the calorific value of the sludge is low, auxiliary fuel 7 is used during combustion. In the example of the present invention, the following (1
) A reaction like (2) occurs.

50a−) 40H″+3HPCk −5−Oas(O
H) (Po4)s +3H20・・・・・・(1) 01L (OH)4 +  2H3PO4→Oa (H
l PO4)z’ 2H20・・・・・・(2) 即ち、リン酸化合物は、リン酸カルシウムへ変化し、そ
の結果スラッジの灰融点の低下もなくまた付着性も増加
しない状態で焼却が可能となる。それにより、媒体相互
間の付着、タリンカ化も発生せず、更に第1図に示すフ
ライアッシュを含む排ガス8を処理する排ガス設備9に
おいてもアッシュの付着を生ぜずに安定した焼却処理が
可能となる。
50a-) 40H''+3HPCk -5-Oas(O
H) (Po4)s +3H20・・・・・・(1) 01L (OH)4 + 2H3PO4→Oa (H
l PO4)z' 2H20 (2) That is, the phosphoric acid compound changes to calcium phosphate, and as a result, it becomes possible to incinerate the sludge without lowering its ash melting point or increasing its adhesion. . As a result, adhesion between the media and formation of slag do not occur, and stable incineration processing is also possible without adhesion of ash in the exhaust gas equipment 9 that processes the exhaust gas 8 containing fly ash shown in Fig. 1. Become.

また本発明により、従来流動層炉で問題となつだリン化
合物と流動媒体中のSiOとの反応によるリン酸ガラス
の形成も、上記したリン酸カルシウムへの変化により、
防止することができ、媒体のタリンカ化の問題が解消す
る。
In addition, the present invention eliminates the formation of phosphate glass due to the reaction between phosphorus compounds and SiO in the fluidized medium, which has been a problem in conventional fluidized bed furnaces, by changing it to calcium phosphate as described above.
This eliminates the problem of the media becoming tarnished.

本発明を実施するに当り、カルシウム化合物のスラッジ
への添加量は、含有されるリンの量によって左右される
べきである。しかし、スラッジ中のリン量の連続分析は
、現在の計測技術では不可能であり、他の手段が望まれ
る。
In practicing the present invention, the amount of calcium compound added to the sludge should depend on the amount of phosphorus contained. However, continuous analysis of the amount of phosphorus in sludge is not possible with current measurement techniques, and other means are desired.

第2図は制御方法の一例を示す。FIG. 2 shows an example of a control method.

良好な流動化を行っている流動層の温度)ま、流動層の
各所でほぼ均一であり、発明者等の経験では+、10℃
程度の偏差しかない。逆に媒体付着あるいはタリンカ生
成等により媒体の流動化が悪くなると、特に流動層上、
下部の温度差が大きくなり、この状態が進行すると最終
的に流動化運動が停止する。すなわち流動化が悪くなる
と、土層部は燃焼により昇温し、下層部は流動化空気に
より冷却され、層と下部での温度差が大きくなってくる
The temperature of a fluidized bed with good fluidization) is almost uniform throughout the fluidized bed, and in the experience of the inventors, the temperature is approximately +10°C.
There is only a slight deviation. On the other hand, if the fluidization of the medium deteriorates due to media adhesion or tarinka formation, etc., especially on the fluidized bed,
As the temperature difference at the bottom increases and this condition progresses, the fluidization movement eventually stops. In other words, when fluidization deteriorates, the temperature of the soil layer increases due to combustion, and the lower layer is cooled by fluidizing air, resulting in a larger temperature difference between the layer and the lower layer.

第2図は、カルシウム化合物の供給方法の一例を示し、
流動層上部温度信号11と流動層下部温度信号12とを
検出し、その温度差13が設定値より大となれば、判定
器14を介して供給量調節計15によりカルシウム化合
物3の量を増加させまた逆に設定値内であれば、段階的
にカルシウム化合物3の添加量を減少させる。それによ
り常にカルシウム化合物の添加量を最適化することが可
能となる。
FIG. 2 shows an example of a method for supplying calcium compounds,
The fluidized bed upper temperature signal 11 and the fluidized bed lower temperature signal 12 are detected, and if the temperature difference 13 between them is larger than the set value, the amount of calcium compound 3 is increased by the supply amount controller 15 via the determiner 14. On the other hand, if it is within the set value, the amount of calcium compound 3 added is gradually decreased. This makes it possible to always optimize the amount of calcium compound added.

く実験例〉 リンを2%(含水ベース)含む食品排水スラッジを焼却
した場合、カルシウム化合物(炭酸カルシウム)を添加
しない従来方法では流動層温度として約800℃で約4
時間焼却したのちの流動層内には媒体が固着結合した状
態が一部みられた。一方、本発明による運転、即ち炭酸
カルシウムを含水スラッジ1Kg当り0.1Kg添加混
練後、焼却した場合、4時間後の流動媒体は何らの付着
、タリンカ化の状況を呈せず、更に長時間の運転が可能
であった。
Experimental Example> When food wastewater sludge containing 2% phosphorus (water content basis) is incinerated, the fluidized bed temperature is approximately 400°C at approximately 800°C in the conventional method without adding calcium compounds (calcium carbonate).
After incineration for a period of time, some parts of the fluidized bed were observed to have a fixed bond of media. On the other hand, in the operation according to the present invention, that is, when 0.1 kg of calcium carbonate is added per 1 kg of water-containing sludge and then incinerated, the fluidized medium after 4 hours does not exhibit any adhesion or tarinka state, and even after a long period of time, It was possible to drive.

〈効果〉 本発明は以上の溝成となっているので、流動媒体の相互
間の付着及び溶融タリンカの防止が図れ、安定した流動
焼却運転が可能となる。
<Effects> Since the present invention has the above-mentioned groove structure, it is possible to prevent adhesion of fluidized media to each other and to prevent molten tarlinker, and stable fluidized incineration operation is possible.

またフライアッシュの付着性が緩和され、炉壁及び後続
のガス処理設備への灰の付着、閉塞が防止される。
In addition, the adhesion of fly ash is alleviated, and adhesion and clogging of ash to the furnace wall and subsequent gas treatment equipment is prevented.

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

第1図は本発明方法の実施例を示す流動層燃焼方法の系
統図、第2図はカルシウム化合物の供給量調節方法を示
す制御系統図である。 1・・・・・・スラッジ   3・・・・・・カルシウ
ム化合物4・・・・・・流動層炉  6・・・・・・流
動媒体11・・・・・・流動層上部温度 12・・・・・・流動層下部温度 第1図 第2図 12 np慝度酌
FIG. 1 is a system diagram of a fluidized bed combustion method showing an embodiment of the method of the present invention, and FIG. 2 is a control system diagram showing a method of adjusting the supply amount of calcium compounds. 1... Sludge 3... Calcium compound 4... Fluidized bed furnace 6... Fluidized medium 11... Fluidized bed top temperature 12... ...Fluidized bed lower temperature Figure 1 Figure 2 Figure 12 np tolerance

Claims (1)

【特許請求の範囲】 1、リン分を含有する物質を流動層炉で燃焼させる方法
において、少くとも燃焼時までに、このリン含有物質に
対してカルシウム化合物を添加することを特徴とするリ
ン含有物質の燃焼方法。 2、流動層の上層と下層の温度差を検出し、この温度差
の大小に対応してカルシウム化合物添加量を調節するよ
う構成したことを特徴とする特許請求の範囲第1項記載
のリン含有物質の燃焼方法。
[Claims] 1. A method for burning a phosphorus-containing substance in a fluidized bed furnace, characterized in that a calcium compound is added to the phosphorus-containing substance at least before combustion. How to burn substances. 2. The phosphorus-containing device according to claim 1, characterized in that the temperature difference between the upper layer and the lower layer of the fluidized bed is detected, and the amount of calcium compound added is adjusted in accordance with the magnitude of this temperature difference. How to burn substances.
JP11548285A 1985-05-30 1985-05-30 Burning of phosphorus-containing substance Granted JPS61276617A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11548285A JPS61276617A (en) 1985-05-30 1985-05-30 Burning of phosphorus-containing substance

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11548285A JPS61276617A (en) 1985-05-30 1985-05-30 Burning of phosphorus-containing substance

Publications (2)

Publication Number Publication Date
JPS61276617A true JPS61276617A (en) 1986-12-06
JPH0523330B2 JPH0523330B2 (en) 1993-04-02

Family

ID=14663609

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11548285A Granted JPS61276617A (en) 1985-05-30 1985-05-30 Burning of phosphorus-containing substance

Country Status (1)

Country Link
JP (1) JPS61276617A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015213885A (en) * 2014-05-12 2015-12-03 株式会社日水コン Method for evaluating risk in clogging of incinerator and method for preventing clogging of incinerator
JP2016128162A (en) * 2015-12-16 2016-07-14 株式会社日水コン Method for preventing clogging of incinerator
JP2019171302A (en) * 2018-03-28 2019-10-10 三機工業株式会社 Sludge incineration equipment and sludge incineration method
JP2019171303A (en) * 2018-03-28 2019-10-10 三機工業株式会社 Sludge incineration equipment and sludge incineration method

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52101871A (en) * 1976-02-24 1977-08-26 Idemitsu Kosan Co Waste sludge incineration method
JPS52113566A (en) * 1976-03-22 1977-09-22 Toray Ind Inc Method of recoverying phosphorous contents from active sludge

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52101871A (en) * 1976-02-24 1977-08-26 Idemitsu Kosan Co Waste sludge incineration method
JPS52113566A (en) * 1976-03-22 1977-09-22 Toray Ind Inc Method of recoverying phosphorous contents from active sludge

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015213885A (en) * 2014-05-12 2015-12-03 株式会社日水コン Method for evaluating risk in clogging of incinerator and method for preventing clogging of incinerator
JP2016128162A (en) * 2015-12-16 2016-07-14 株式会社日水コン Method for preventing clogging of incinerator
JP2019171302A (en) * 2018-03-28 2019-10-10 三機工業株式会社 Sludge incineration equipment and sludge incineration method
JP2019171303A (en) * 2018-03-28 2019-10-10 三機工業株式会社 Sludge incineration equipment and sludge incineration method

Also Published As

Publication number Publication date
JPH0523330B2 (en) 1993-04-02

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