JPS5945948A - Use of waste fluidized medium from fluidized bed boiler - Google Patents

Use of waste fluidized medium from fluidized bed boiler

Info

Publication number
JPS5945948A
JPS5945948A JP15505582A JP15505582A JPS5945948A JP S5945948 A JPS5945948 A JP S5945948A JP 15505582 A JP15505582 A JP 15505582A JP 15505582 A JP15505582 A JP 15505582A JP S5945948 A JPS5945948 A JP S5945948A
Authority
JP
Japan
Prior art keywords
waste
fluidized bed
bed boiler
fluidized
cement
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
Application number
JP15505582A
Other languages
Japanese (ja)
Inventor
鈴木 信次郎
紀久士 常吉
太尾田 清通
村上 光春
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 Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP15505582A priority Critical patent/JPS5945948A/en
Publication of JPS5945948A publication Critical patent/JPS5945948A/en
Pending legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 流動層ボイラは1次のような優れた特徴を有しており、
今後の発電用ボイラの新しい方向として注目されている
[Detailed description of the invention] The fluidized bed boiler has the following excellent characteristics:
This is attracting attention as a new direction for power generation boilers in the future.

Q) 伝熱係数が従来形ボイラに比して5〜IO倍人き
(とれるため、ボイラがコンlfクトにでき  る 。
Q) The heat transfer coefficient is 5 to IO times higher than that of conventional boilers, so the boiler can be made compact.

(リ 流動顔向に石灰石、生石灰、あるいは消石灰を混
入することにより、高温直接脱硫が可能で、排煙脱硫装
置の省略、もしくは小規模化が可能である。
(Re) By mixing limestone, quicklime, or slaked lime in the flow direction, high-temperature direct desulfurization is possible, making it possible to omit or downsize the flue gas desulfurization equipment.

■ 燃焼潤度がsoo 〜900 ’<、:と低いため
、 NOxの生成が少なく、脱硝設備が必要ないか、あ
るいは必要な場合も脱硝にザする費用が′ムい。
■ Since the combustion moisture level is as low as ~900', NOx is produced less, and denitrification equipment is not required, or even if it is necessary, the cost of denitrification is low.

また石炭灰の溶融が起らず、取扱いがfluな十、材料
の高温11に食がなく、伝熱管にIt!I価な材料を使
う必要がない。
In addition, coal ash does not melt, handling is fluid, and there is no corrosion due to the high temperature of the material. There is no need to use I-valent materials.

■ 例えば石炭を燃料とする場合、 (Jl、給する燃
料石炭の゛1乙均粒径が大きいので、その粉砕のための
動力が小さくてすむ。即ち微粉炭燃焼時200メツツユ
残約15%に対し、′tk、動層ボイラは5〜6 mm
以下で良い。
■ For example, when coal is used as fuel, (Jl), the average particle size of the supplied fuel coal is large, so the power required for pulverization is small. In other words, when pulverized coal is burned, the remaining 200 m² is about 15%. On the other hand, 'tk, moving bed boiler has a diameter of 5 to 6 mm.
The following is fine.

しかしこの流動層ボイラも次の問題を自しており、これ
の解決が実用化への大きな問題である。すなわち流Ev
J屑ボイラの流動媒体皮ひ脱硫媒体としての右灰イ1.
生石灰または消−/i灰から生成するOaOが燃焼カス
中の802と反応してOa S O4が生成する。これ
は流動層ボイラ外にJIQ出してOaOに14 /、t
!L楯環使用する方法はあるが。
However, this fluidized bed boiler also has the following problems, and solving them is a major problem for practical use. In other words, flow Ev
Right gray as a fluidized medium skin desulfurization medium for J scrap boiler 1.
OaO produced from quicklime or slaked/i ash reacts with 802 in the combustion residue to produce Oa SO4. This is taken out of the JIQ outside the fluidized bed boiler and transferred to OaO at 14/, t.
! There is a way to use the L shield ring.

++1生王稈に要する費用が1lIIr+lliてあり
経済的に成り☆だない。
The cost required for ++1 raw king culm is 1lIIr+lli, so it is not economically viable.

また脱硫を十分性わせるためにはOa分■1として08
分と燃料石炭中の8分のモル比Oa/S≧2が必四であ
り、このため流動層の廃棄物中にはOdOが多ntに含
まれており、このままノイコ棄すると強いアルカ!J 
+’lを示し公害上問題がある。また中和して廃棄する
にも多量の中和剤が必要である。
In addition, in order to ensure sufficient desulfurization, the Oa fraction ■1 should be set to 08
It is essential that the molar ratio Oa/S≧2 between minute and 8 minutes in the fuel coal is 2. Therefore, the fluidized bed waste contains a large amount of OdO, and if it is discarded as it is, it will become a strong alkali! J
+'l, which poses a pollution problem. Furthermore, a large amount of neutralizing agent is required to neutralize and dispose of the product.

本発明は、−1−記諸問題を解決するため提案されたも
ので、−I:、tC石炭だき流動層ボイラの脱硫媒体と
して使用した廃石灰(0aSO4、OaOの混り物)並
びに生成した石炭灰の混合物をセメントプラントに投入
rることにより、廃石灰と石炭灰の処理、並びにセメン
トプラントの熱経済面でのメリットをイfする流動層ボ
イラのj介棄媒体処却方法に関する。
The present invention was proposed to solve the problems listed in -1-. This invention relates to a method for disposing waste media in a fluidized bed boiler, which processes waste lime and coal ash and takes advantage of the thermoeconomic aspects of a cement plant by introducing a mixture of coal ash into a cement plant.

本発明方法は商業ベースの発電プラノI・、 −、]f
=びにセメノドプラントにおいて物質収支的にまた七メ
ノト製品品負1からみて1−分成り)’l−)ものであ
る。
The method of the present invention can be used for commercial power generation plano I・, −, ]f
In terms of material balance and in terms of material balance in the Semenodo plant, it is composed of 1-component (1-)'l-) from the viewpoint of the product quality of the seven products.

次に本発明77法を実施例を参照して、1γ細に説明す
る。
Next, the 77 method of the present invention will be explained in detail with reference to Examples.

第1表は発電規模100〇八11v、並Cノ・にヒメノ
トノ1−産[i 2000 T/1」規模のブラットの
物質11V tを小す。
Table 1 shows that the power generation scale is 10008 11V, and the Blatt's material 11V t of the size of 2000 T/1 produced in Himenotono 1-[i 2000 T/1] is small.

第1表の10100Oの17f1.両層発電プラノi・
より発生する廃棄媒体を2000 ’i’/Elのピメ
ノ)・プラノ)・に原料として全量供給した場合の実施
1!/11を第3表に示す。
17f1 of 10100O in Table 1. Double layer power generation Plano i・
Implementation 1 when the entire amount of waste media generated from 2000 'i'/El is supplied as raw material to Pimeno) and Plano). /11 is shown in Table 3.

第2表は使用原料の組成を示す。Table 2 shows the composition of the raw materials used.

第3表から廃棄媒体全1■をセメノドプラットに供給し
ても,係数個,クリツカ組成及びクリ7カ鉱物組成共に
廃棄媒体を使用しない比較例と変わりなり,1−公使用
できることが明らかである。廃棄媒体の使用によ−って
軟けい(iや,鉄原料の使用量が上昇するが,逆に粘土
の使用h(がそれにも増して減少する。またf! 、、
0はセメント原料の大部分を占める自沃Y−+の一++
1fとして利用でき,石灰石の様に熱分解による吸熱が
ないのでセメン]・焼成熱量の節減に役立つ。また石こ
うから供給されるS08により生産されるクリツカ(約
2000 T/l−1 )中+7) 808が045重
fit%となるが,この程度であれば運転上のトラブル
もなく1−公使用可能である。
From Table 3, it is clear that even if all 1■ of waste media is supplied to Semenodoplat, the coefficient, Kritka composition, and K7K mineral composition will be different from the comparative example in which no waste media is used, and it can be used publicly. be. By using waste media, the usage of soft silica (i) and iron raw materials increases, but conversely, the usage of clay (h) decreases even more.
0 is 1++ of the natural Y-+ which accounts for most of the cement raw materials
It can be used as 1f, and unlike limestone, it does not absorb heat due to thermal decomposition, so it is useful for reducing the amount of heat used in calcination. In addition, the Kritsuka (approximately 2000 T/l-1) 808 produced by S08 supplied from gypsum has a 045 weight fit%, but at this level it can be used publicly without any operational troubles. It is.

このように流動層発電プラントの流動層廃棄媒体をセメ
ント原料として使用することは,流動層ボイラの最大の
問題である脱硫用石灰の処理問題を完全に解決してくれ
るとともに,石炭灰の処理も合イつせて解決してくれる
。また七メツドブラントからみると,原料の一部を廃棄
物で代替することとなり,セメントコストの低減に役立
つ。
In this way, the use of fluidized bed waste media from fluidized bed power plants as a raw material for cement completely solves the problem of disposing of lime for desulfurization, which is the biggest problem with fluidized bed boilers, and also solves the problem of disposing of coal ash. They will solve it together. Also, from the point of view of Shichimetsudobunt, some of the raw materials are replaced with waste, which helps reduce cement costs.

実際プラントでは,流動層ボイラから排出される流動層
廃棄媒体はr Ih濡のため適当なiIi1度までドげ
る方が取扱が容易である。またセメント原料にするため
には,数lθμ「nに粒径を小さくする必要があるので
,粉砕が必要であるが,流動層ホイラ内で加熱された後
の6灰Y1−や石炭灰は粉砕され易い状態にあるので,
セメントDルキ1粉砕槻に供給することにより,1分微
粉砕できる。
In actual plants, the fluidized bed waste medium discharged from the fluidized bed boiler is wetted by rIh, so it is easier to handle it if the temperature is lowered to an appropriate temperature of 1°. In addition, in order to use it as a raw material for cement, it is necessary to reduce the particle size to several lθμ'n, so pulverization is necessary, but 6 ash Y1- and coal ash after being heated in a fluidized bed wheeler must be pulverized. Because it is in a state where it is easy to
Cement can be finely pulverized for 1 minute by feeding it to a pulverizer.

第 l 表    物  質  収  支第 2表  
 供  試  原  料 第3表 配合、il算 第1図に本発明の一実施例のブロック線図を示す。流動
層ボイラで燃焼後の石炭灰並ひに脱硫後の石灰よりなる
廃棄媒体は、高温状態で取り出され、 +l1ll熱コ
ンヘヤで熱交換i#Hに運ばれ。
Table l Material Balance Table 2
Table 3: Materials to be Tested Mixture and Il Calculation Figure 1 shows a block diagram of an embodiment of the present invention. The waste medium consisting of coal ash after combustion in the fluidized bed boiler as well as lime after desulfurization is taken out at high temperature and conveyed to the heat exchanger i#H in a +1111 heat conveyor.

ここで冷空気(常l晶で可)で直接8’00 ”(F稈
度以ドに冷却され、コノベヤによりセメン+−h:i 
1+の粉砕機に運ばれる。廃棄媒体は熱交換器通過後も
尚高温であり、かつ粉砕され易い状態にあるので、粉砕
機の形式により、粉砕機への適切な供給位屑が選定でき
る。廃棄媒体は、セメント原料と共に微粉砕され、一般
にカス式輸送管によりセメントプラットに供給される。
Here, it is directly cooled with cold air (ordinary crystal is possible) to a temperature below 8'00'' (F culm), and the cement +-h:i
Transported to 1+ crusher. Since the waste medium is still at a high temperature even after passing through the heat exchanger and is in a state where it is easily crushed, an appropriate amount of waste to be supplied to the crusher can be selected depending on the type of crusher. The waste media is pulverized together with the cement raw material and is generally fed to the cement plat via a waste transfer pipe.

ここで熱交換器は高温廃棄物の取扱い士便宜的においた
ものでなくても特にプロセス上の支障はない。
Here, even if the heat exchanger is not placed for the convenience of the person handling the high-temperature waste, there is no particular problem in the process.

かかる流動層ボイラとセメントプラントとの結合ノステ
ムにより、流動層ボイラでは1介棄媒体の処理の問題が
解消し、セメントプラントではセメントのjjr料及び
熱エネルギの節減となりセメントコスト ので,両者にとー、てイj効なノステムである。
By combining such a fluidized bed boiler and a cement plant, the fluidized bed boiler solves the problem of disposing of one waste medium, and the cement plant saves cement materials and thermal energy, reducing cement costs. , it is a very effective nostem.

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

第1図は本発明方法の一実IjfU iダ[を示すフロ
ーチャー1・である。
FIG. 1 is a flowchart 1 showing one embodiment of the method of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 流動及び脱硫媒体として石灰石、生石灰あるいは消石灰
を用いた流動層ボイラより発生する流動媒体廃棄物をセ
メント原料の一部として使用することを特徴とする流動
層ボイラより発生する廃棄流動媒体の利用方法。
A method of utilizing waste fluid media generated from a fluidized bed boiler, characterized in that the fluidized media waste generated from a fluidized bed boiler using limestone, quicklime or slaked lime as a fluidization and desulfurization medium is used as part of a cement raw material.
JP15505582A 1982-09-06 1982-09-06 Use of waste fluidized medium from fluidized bed boiler Pending JPS5945948A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15505582A JPS5945948A (en) 1982-09-06 1982-09-06 Use of waste fluidized medium from fluidized bed boiler

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15505582A JPS5945948A (en) 1982-09-06 1982-09-06 Use of waste fluidized medium from fluidized bed boiler

Publications (1)

Publication Number Publication Date
JPS5945948A true JPS5945948A (en) 1984-03-15

Family

ID=15597680

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15505582A Pending JPS5945948A (en) 1982-09-06 1982-09-06 Use of waste fluidized medium from fluidized bed boiler

Country Status (1)

Country Link
JP (1) JPS5945948A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61271098A (en) * 1985-05-27 1986-12-01 Babcock Hitachi Kk Incinerating method for waste water sludge
US5766339A (en) * 1997-05-07 1998-06-16 Dravo Lime Company Process for producing cement from a flue gas desulfurization process waste product
US5769940A (en) * 1997-05-07 1998-06-23 Dravo Lime Company Process for producing cement and elemental sulfur from a flue gas desulfurization waste product

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61271098A (en) * 1985-05-27 1986-12-01 Babcock Hitachi Kk Incinerating method for waste water sludge
US5766339A (en) * 1997-05-07 1998-06-16 Dravo Lime Company Process for producing cement from a flue gas desulfurization process waste product
US5769940A (en) * 1997-05-07 1998-06-23 Dravo Lime Company Process for producing cement and elemental sulfur from a flue gas desulfurization waste product

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