JPS63151650A - Method of burning cement clinker - Google Patents

Method of burning cement clinker

Info

Publication number
JPS63151650A
JPS63151650A JP61296759A JP29675986A JPS63151650A JP S63151650 A JPS63151650 A JP S63151650A JP 61296759 A JP61296759 A JP 61296759A JP 29675986 A JP29675986 A JP 29675986A JP S63151650 A JPS63151650 A JP S63151650A
Authority
JP
Japan
Prior art keywords
waste
air
exhaust
equipment
exhaust gas
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
JP61296759A
Other languages
Japanese (ja)
Inventor
平井 祥雄
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.)
IHI Corp
Original Assignee
IHI Corp
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 IHI Corp filed Critical IHI Corp
Priority to JP61296759A priority Critical patent/JPS63151650A/en
Publication of JPS63151650A publication Critical patent/JPS63151650A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • Y02P40/125Fuels from renewable energy sources, e.g. waste or biomass

Landscapes

  • Curing Cements, Concrete, And Artificial Stone (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】 〈産業上の利用分野〉 本発明は都市ゴミ等の廃棄物をセメントクリンカの焼成
用の燃料の一部または全部として使用するセメントクリ
ンカの焼成方法に関する。
DETAILED DESCRIPTION OF THE INVENTION <Industrial Application Field> The present invention relates to a cement clinker firing method that uses waste such as municipal garbage as part or all of the fuel for cement clinker firing.

〈従来技術およびその問題点〉 第2図は従来のセメントクリンカ焼成装置の典型的な一
例を説明する−ためのフローチャートであって、矢印は
ガスの流れを示す。焼成装置は、基本的には、予熱装置
1、ロータリキルン2、クリンカクーラ3によって構成
されている。
<Prior art and its problems> FIG. 2 is a flowchart for explaining a typical example of a conventional cement clinker firing device, in which arrows indicate gas flows. The firing device basically includes a preheating device 1, a rotary kiln 2, and a clinker cooler 3.

この構成において、予熱装置1に投入された原料が予熱
され、キルン2に送入されて焼成され、クーラ3に投下
されて、ここに導入された冷却空気によって冷却され製
品クリンカとなる間に、該冷却空気の一部はキルン2の
燃焼用二次空気として回収され、キルン2の排ガスは予
熱装置1にて原料を予熱した後、設備から排出される。
In this configuration, the raw material input into the preheating device 1 is preheated, sent to the kiln 2 to be fired, and dropped into the cooler 3, where it is cooled by the cooling air introduced there and becomes a product clinker. A part of the cooling air is recovered as secondary air for combustion in the kiln 2, and the exhaust gas from the kiln 2 is discharged from the equipment after preheating the raw material in the preheating device 1.

尚、予熱装置1に原料の仮焼炉1aを設けた設備の場合
には、冷却空気の別の一部はキルン2をバイパスし、二
次空気ダクト4を経て、仮焼炉1aの燃焼用二次空・気
として直接予熱装置1に回収される。
In the case of equipment in which the preheating device 1 is equipped with a raw material calciner 1a, another part of the cooling air bypasses the kiln 2, passes through the secondary air duct 4, and is used for combustion in the calciner 1a. It is directly recovered to the preheating device 1 as secondary air/gas.

予熱装置1から排出される排ガスは、排ガスダクト5か
ら排Jlll 6により吸引され、さらに集じん器7、
集じん器用排風機7aを経て煙突8から大気中に放出さ
れる。また、キルン等の燃焼用二次空気として回収され
る以外の冷却空気は、クーラ3から余剰高温空気として
排出され、排気ダクト9から集じん器10、排風機11
を経て煙突12から大気中に放出される。予熱装置1か
ら排出される排ガスは通常350℃程度の高温であるか
ら、その余熱を利用するために、集゛じん器1に入る前
に乾燥装置13に導入して原料等を乾燥したり、廃熱ボ
イラ14に導入して蒸気を発生し発電したりする。廃熱
ボイラ14による発電は入口ガス温度が高くなるほど効
率が良いから、場合によっては、排ガスダクト5の途中
の位置14aや予熱装置1と並列の位置14bに設置さ
れることもある。
The exhaust gas discharged from the preheating device 1 is sucked from the exhaust gas duct 5 by the exhaust gas duct 6, and is further passed through the dust collector 7,
It is discharged into the atmosphere from the chimney 8 through the dust collector exhaust fan 7a. Cooling air other than that recovered as secondary air for combustion in a kiln or the like is discharged from the cooler 3 as surplus high-temperature air, and is passed through the exhaust duct 9 to the dust collector 10 and the exhaust fan 11.
It is then released into the atmosphere from the chimney 12. The exhaust gas discharged from the preheating device 1 is normally at a high temperature of about 350°C, so in order to utilize the residual heat, it is introduced into the drying device 13 to dry raw materials etc. before entering the dust collector 1. The waste heat is introduced into the waste heat boiler 14 to generate steam and generate electricity. Since power generation by the waste heat boiler 14 is more efficient as the inlet gas temperature increases, depending on the case, it may be installed at a position 14a in the middle of the exhaust gas duct 5 or at a position 14b parallel to the preheating device 1.

しかし、クーラ3から排出される余剰空気については、
普通の状態でも温度が150〜250℃程度の範囲で変
化するうえに量的にも変動が大きいので、余熱を利用す
る場合に比較的不安定であり容易ではない。それでも、
補助的に乾燥熱源として利用されたりする場合があるが
、使用量としてはあまり多くなく余剰分は集じん後大気
中に放散しているが、ここに含有されているダストは比
較釣果じんが困難であり、かつ、付近の物品に容易に付
着固結するので問題を起こすことが多い。また、最近、
省エネルギが強く言われるようになってからは、このよ
うな熱源でさえも廃熱発電に利用するようなことが実施
されているが、比較的低温度のガスを導入するというこ
とは装置の効率を低下させることにもなり、多額の投資
に対して十分な効果が期待できないということにもなる
However, regarding the excess air discharged from cooler 3,
Even in normal conditions, the temperature changes within a range of about 150 to 250°C, and the amount also varies greatly, so it is relatively unstable and difficult to use residual heat. nevertheless,
Although it is sometimes used as an auxiliary drying heat source, the amount used is not very large and the surplus is released into the atmosphere after dust collection, but the dust contained here is difficult to compare. Moreover, it often causes problems because it easily adheres to and hardens on nearby objects. Also, recently,
Since energy conservation has become a strong priority, even such heat sources have been used for waste heat power generation, but introducing relatively low temperature gas means that equipment It also reduces efficiency and means that a sufficient effect cannot be expected from a large investment.

一方、都市ゴミ等廃棄物の処理に関して種々の問題が提
起されている。各種廃棄物による埋立の場所が少なくな
って行き、これら廃棄物の処理施設の拡充は急を要する
問題となっている。
On the other hand, various problems have been raised regarding the treatment of waste such as municipal garbage. Landfill sites for various types of waste are becoming fewer and fewer, and the expansion of treatment facilities for these wastes has become an urgent issue.

これらの廃棄物は通常焼却処理されており、そこから発
生する廃熱は発電に利用されて、設備の電力を補ったり
、給湯のような形で地域の福祉に貢献したりしている場
合が少なくない。
These wastes are usually incinerated, and the waste heat generated is sometimes used to generate electricity to supplement electricity for equipment or contribute to local welfare in ways such as hot water supply. Not a few.

しかし、いずれの場合にも、これら処理施設の建設や運
転維持には膨大な費用を必要とするばかりではなく、臭
気の発生や汚物汚水による環境汚染の問題から、施設を
建設すること自体が地域住民の同意を得られないという
ような事態にまで至っており、施設の拡充が思うように
捗っていないのが実状である。
However, in either case, not only does the construction and operation and maintenance of these treatment facilities require a huge amount of money, but the construction of the facilities itself is difficult for the local community due to the problems of odor and environmental pollution caused by sewage. The reality is that the expansion of facilities is not progressing as expected, as the consent of residents has not been obtained.

〈発明の目的〉 本発明は以上の点に鑑みてなされたもので、セメントタ
リンカ焼成設備と廃棄物の処理設備を有機的に結合して
、省エネルギと環境汚染防止、さらに建設費の削減まで
も図れるセメントタリンカ焼成方法を提供することを目
的とする。
<Purpose of the Invention> The present invention has been made in view of the above points, and aims to save energy, prevent environmental pollution, and reduce construction costs by organically combining cement tarinka firing equipment and waste processing equipment. It is an object of the present invention to provide a cement tarinka firing method that can achieve even the highest possible results.

く問題点を解決するための手段〉 上記目的を達成するため本発明のセメントクリンカの焼
成方法は、都市ゴミ等の廃棄物を乾燥装置に収容し、該
乾燥装置にクリンカクーラの高温空気の一部を導入し、
その排気をクリンカクーラに再び戻し、該乾燥装置の排
気が混ったクリンカクーラの高温空気をロータリキルン
または仮焼炉の燃焼用空気として使用することを特徴と
するものである。
Means for Solving the Problems In order to achieve the above object, the cement clinker firing method of the present invention stores waste such as municipal garbage in a drying device, and supplies part of the high-temperature air from a clinker cooler to the drying device. Introducing the
The exhaust gas is returned to the clinker cooler, and the high-temperature air from the clinker cooler mixed with the exhaust air from the drying device is used as combustion air for the rotary kiln or calciner.

く実 施 例〉 以下本発明を具体化した一実施例を図面を参照しつつ説
明する。第1図は本発明の方法を具体化した装置のフロ
ーチャートである。第1図において 1は予熱装置、1
aは仮焼炉、2はロータリキルン、3はクリンカクーラ
、4は二次空気ダクト、5は排ガスダクト、6は排風機
、7は集じん器、7aは集じん器用排風機、8は煙突、
9は排気ダクト、9aは分岐排気ダクト、10は集じん
器、11は集じん器用排風機、12は煙突、13は乾燥
装置、14は廃熱ボイラ、15は廃棄物の乾燥機、16
は集じん器、17は排風機、18は排気ダクトである。
Embodiment> An embodiment embodying the present invention will be described below with reference to the drawings. FIG. 1 is a flowchart of an apparatus embodying the method of the invention. In Fig. 1, 1 is a preheating device, 1
a is a calcining furnace, 2 is a rotary kiln, 3 is a clinker cooler, 4 is a secondary air duct, 5 is an exhaust gas duct, 6 is an exhaust fan, 7 is a dust collector, 7a is an exhaust fan for the dust collector, 8 is a chimney ,
9 is an exhaust duct, 9a is a branch exhaust duct, 10 is a dust collector, 11 is an exhaust fan for the dust collector, 12 is a chimney, 13 is a drying device, 14 is a waste heat boiler, 15 is a waste dryer, 16
17 is a dust collector, 17 is an exhaust fan, and 18 is an exhaust duct.

尚第1図は第2図に示す従来のセメントクリンカの焼成
装置に廃棄物乾燥機15等を付加したもので、その他の
部分については第2図と同様なので、同一の部分につい
ては同じ符号を用いてあって、説明を省略し、第1図に
おいて新たに付加した部分につき説明する。
Figure 1 shows the conventional cement clinker firing equipment shown in Figure 2 with a waste dryer 15 added, and other parts are the same as Figure 2, so the same parts are designated by the same reference numerals. The newly added parts in FIG. 1 will be explained below, and the explanation will be omitted.

廃棄物の乾燥機15はロータリ一式、グレード式等の形
式のものがあり、廃棄物と熱風とを直接接触させて、濡
れた廃棄物を乾燥させる。排風機17は廃棄物の乾燥に
使用された熱風を吸引して、排気ダクト18を通じて再
びクリンカクーラ3に戻す。集じん器16は排Jill
l17に異物が飛込まないように設けられている。
The waste dryer 15 is of a type such as a rotary set or a grade type, and it dries wet waste by bringing the waste into direct contact with hot air. The exhaust fan 17 sucks the hot air used for drying the waste and returns it to the clinker cooler 3 through the exhaust duct 18. The dust collector 16 is an exhaust
It is provided to prevent foreign matter from entering l17.

以下作用を説明する。The action will be explained below.

上記した構成にすることにより、クーラ3の余剰高温空
気の一部は、分岐ダクト9aから乾燥機15に流入し廃
棄物の乾燥に利用されるようになる。廃棄物を乾燥した
後の排気は強い臭気を有するので、脱臭してやる必要が
ある。この排気は700℃以上程度に加熱してやれば脱
臭することができる。そこでこれをキルン2等の燃焼用
空気として回収利用し、脱臭を図るようにする。しかし
、通常はこの排気温度(100〜150℃)はそのまま
キルン2等に導入するには低過ぎるので集じん器16、
排風機17を経由して排気ダクト18によってクーラ3
に冷却空気として導入する。冷却空気としては、通常は
常温空気が導入されているから、その意味ではこの温度
は逆に高いが、従来の方法でも同程度の温度の余剰排気
を循環使用して熱回収効率の向上を図ろうとしているよ
うな例もあり、特に問題にはならない。ざらに、余剰排
気量は燃焼空気量に対して通常は1:1〜1.2(変動
の極限値としては1.5倍程度になることもあるが)程
度であるのでほとんど全量を回収使用することができる
With the above configuration, a part of the excess high temperature air of the cooler 3 flows into the dryer 15 from the branch duct 9a and is used for drying the waste. Since the exhaust gas after drying the waste has a strong odor, it is necessary to deodorize it. This exhaust gas can be deodorized by heating it to about 700°C or higher. Therefore, this air is recovered and used as combustion air for the kiln 2, etc., to deodorize it. However, normally, this exhaust temperature (100 to 150°C) is too low to directly introduce it into the kiln 2, etc., so the dust collector 16,
Cooler 3 via exhaust fan 17 and exhaust duct 18
is introduced as cooling air. Room-temperature air is usually introduced as cooling air, so in that sense the temperature is high, but even with conventional methods, surplus exhaust gas at a similar temperature can be circulated and used to improve heat recovery efficiency. There are some cases where people are trying to do so, so this is not a particular problem. Roughly speaking, the amount of excess exhaust gas is usually about 1:1 to 1.2 (although it may be about 1.5 times the amount of combustion air), so almost all of it is recovered and used. can do.

尚、乾燥機15から排出される乾燥された廃棄物は、必
要に応じて不燃物を分離し、適当に粉砕された後、キル
ン2や予熱装置1内の仮焼炉1aの燃料として使用され
る。
Incidentally, the dried waste discharged from the dryer 15 is used as fuel for the kiln 2 and the calciner 1a in the preheating device 1 after separating incombustible materials as necessary and pulverizing it appropriately. Ru.

乾燥機15からの排気の回収方法は上記に限定されるも
のではなく、例えば、キルン2の一時空気として使用し
たり、仮焼炉の二次空気に混入したりすることも可能で
ある。また、廃棄物の水分が多く余剰空気の熱量が不足
する場合は、予熱装置排ガスを利用するとか助燃してや
るとかの方法もある。尚、設備休転時の臭気発生防止が
必要な場合には、排気ダクト18中に緊忠避難用として
脱臭材等を配備しておけばよい。
The method of recovering the exhaust gas from the dryer 15 is not limited to the above, and for example, it can be used as temporary air for the kiln 2 or mixed into the secondary air of the calciner. Additionally, if the waste contains a lot of water and the excess air does not have enough heat, there are other methods such as using preheater exhaust gas or auxiliary combustion. Incidentally, if it is necessary to prevent the generation of odor when the equipment is not in operation, a deodorizing material or the like may be provided in the exhaust duct 18 for use in evacuation.

〈発明の効果〉 以上に述べた本発明の効果をまとめてみると、下記のよ
うになる。
<Effects of the Invention> The effects of the present invention described above can be summarized as follows.

(1)  従来大気中に放散していた余剰熱量を活用し
て廃棄物の乾燥を行い、それによって回収される資源を
燃料として再使用することにより、二重の省エネルギ効
果が得られる。
(1) A double energy-saving effect can be obtained by drying waste by utilizing the surplus heat that was conventionally dissipated into the atmosphere and reusing the recovered resources as fuel.

■ 廃熱ボイラのように、特に法的点検を要求されるよ
うな面倒な設備を用いずに余熱の回収ができる。
■ Remaining heat can be recovered without using complicated equipment that requires legal inspection, unlike waste heat boilers.

■ 脱臭、集じん等が比較的容易に行える環境が、技術
的にも整っている。
■ The environment in which deodorization and dust collection can be carried out relatively easily is technically in place.

(4)  セメント焼成設備と廃棄物処理施設が相互補
完して二重投資が回避されるので、建設費が大巾に削減
できる。
(4) Construction costs can be drastically reduced because cement firing equipment and waste treatment facilities complement each other and double investment is avoided.

■ セメントプラント中に合理化、生産調整等による遊
休設備がある場合には、そのうちのほとんどの設備を有
効に再生活用することができるので、さらに建設費を削
減することができるが、さらにそればかりではなく、廃
棄物処理施設の設置場所に係る問題の解決までも容易に
できる可能性を期待できる。
■ If there is idle equipment in a cement plant due to rationalization or production adjustment, most of that equipment can be effectively recycled and used, which can further reduce construction costs, but it is not enough to do so alone. In addition, it is expected that it will be possible to easily solve problems related to the location of waste treatment facilities.

(ω 人員や機器の二重配備が回避されるので、人件費
や機器の保守点検等の運転維持費用が大巾に節減可能な
る。
(ω) Since redundant deployment of personnel and equipment is avoided, personnel costs and operation and maintenance costs such as equipment maintenance and inspection can be significantly reduced.

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

第1図は本発明の一実施例のフローチャー1・、第2図
は従来のセメントタリンカ焼成装置のフロ・−チャート ド・・・・・予熱装置 2・・・・・・ロータリキルン 3・・・・・・クリンカクーラ
Fig. 1 is a flowchart 1 of an embodiment of the present invention, and Fig. 2 is a flowchart of a conventional cement tarinka firing apparatus...Preheating device 2...Rotary kiln 3・・・・・・Clinker cooler

Claims (1)

【特許請求の範囲】[Claims] 都市ゴミ等の廃棄物を乾燥装置に収容し、該乾燥装置に
クリンカクーラの高温空気の一部を導入し、その排気を
クリンカクーラに再び戻し、該乾燥装置の排気が混った
クリンカクーラの高温空気をロータリキルンまたは仮焼
炉の燃焼用空気として使用することを特徴とするクリン
カクーラの焼成方法。
Waste such as municipal garbage is stored in a drying device, a part of the high-temperature air from the clinker cooler is introduced into the drying device, and the exhaust air is returned to the clinker cooler, and the clinker cooler mixed with the exhaust air from the drying device is A clinker cooler firing method characterized in that high-temperature air is used as combustion air in a rotary kiln or calciner.
JP61296759A 1986-12-15 1986-12-15 Method of burning cement clinker Pending JPS63151650A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61296759A JPS63151650A (en) 1986-12-15 1986-12-15 Method of burning cement clinker

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61296759A JPS63151650A (en) 1986-12-15 1986-12-15 Method of burning cement clinker

Publications (1)

Publication Number Publication Date
JPS63151650A true JPS63151650A (en) 1988-06-24

Family

ID=17837750

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61296759A Pending JPS63151650A (en) 1986-12-15 1986-12-15 Method of burning cement clinker

Country Status (1)

Country Link
JP (1) JPS63151650A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003506299A (en) * 1999-07-30 2003-02-18 エフ・エル・スミス・アンド・カンパニー・エー・エス Method and apparatus for incinerating combustible waste during the production of cement clinker
JP2006035189A (en) * 2004-07-30 2006-02-09 Taiheiyo Cement Corp Method for treating organic sludge utilizing cement production process
JP2006175356A (en) * 2004-12-22 2006-07-06 Sumitomo Osaka Cement Co Ltd Processing method of chicken droppings and treatment apparatus
JP2006212594A (en) * 2005-02-07 2006-08-17 Ube Ind Ltd Method for treating exhaust gas generated when waste is dried
JP2006272289A (en) * 2005-03-30 2006-10-12 Sumitomo Osaka Cement Co Ltd Treating method of organic waste
WO2008001746A1 (en) 2006-06-28 2008-01-03 Taiheiyo Cement Corporation Cement calcination apparatus and method of drying highly hydrous organic waste
WO2008001747A1 (en) 2006-06-28 2008-01-03 Taiheiyo Cement Corporation Cement burning apparatus and method of drying highly hydrous organic waste
JP2011079709A (en) * 2009-10-08 2011-04-21 Taiheiyo Cement Corp Method and apparatus for converting waste into cement fuel
JP2012192389A (en) * 2011-03-18 2012-10-11 Taiheiyo Cement Corp Treatment method of fine powder containing chlorine and lead
EP2735554A1 (en) * 2012-11-22 2014-05-28 Lafarge Process and equipment for drying solid wastes using gas from cement clinker cooler

Cited By (16)

* Cited by examiner, † Cited by third party
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JP4721601B2 (en) * 1999-07-30 2011-07-13 エフ・エル・スミス・アンド・カンパニー・エー・エス Method and apparatus for incineration of combustible waste during the manufacture of cement clinker
JP2003506299A (en) * 1999-07-30 2003-02-18 エフ・エル・スミス・アンド・カンパニー・エー・エス Method and apparatus for incinerating combustible waste during the production of cement clinker
JP2006035189A (en) * 2004-07-30 2006-02-09 Taiheiyo Cement Corp Method for treating organic sludge utilizing cement production process
JP2006175356A (en) * 2004-12-22 2006-07-06 Sumitomo Osaka Cement Co Ltd Processing method of chicken droppings and treatment apparatus
JP2006212594A (en) * 2005-02-07 2006-08-17 Ube Ind Ltd Method for treating exhaust gas generated when waste is dried
JP2006272289A (en) * 2005-03-30 2006-10-12 Sumitomo Osaka Cement Co Ltd Treating method of organic waste
KR101354968B1 (en) * 2006-06-28 2014-01-24 다이헤이요 엔지니어링 가부시키가이샤 Cement burning apparatus and method of drying highly hydrous organic waste
EP2039660A1 (en) * 2006-06-28 2009-03-25 Taiheiyo Cement Corporation Cement calcination apparatus and method of drying highly hydrous organic waste
WO2008001747A1 (en) 2006-06-28 2008-01-03 Taiheiyo Cement Corporation Cement burning apparatus and method of drying highly hydrous organic waste
EP2039660A4 (en) * 2006-06-28 2011-08-03 Taiheiyo Cement Corp Cement calcination apparatus and method of drying highly hydrous organic waste
WO2008001746A1 (en) 2006-06-28 2008-01-03 Taiheiyo Cement Corporation Cement calcination apparatus and method of drying highly hydrous organic waste
KR101354966B1 (en) * 2006-06-28 2014-01-24 다이헤이요 엔지니어링 가부시키가이샤 Cement calcination apparatus and method of drying highly hydrous organic waste
JP2011079709A (en) * 2009-10-08 2011-04-21 Taiheiyo Cement Corp Method and apparatus for converting waste into cement fuel
JP2012192389A (en) * 2011-03-18 2012-10-11 Taiheiyo Cement Corp Treatment method of fine powder containing chlorine and lead
EP2735554A1 (en) * 2012-11-22 2014-05-28 Lafarge Process and equipment for drying solid wastes using gas from cement clinker cooler
WO2014079915A1 (en) * 2012-11-22 2014-05-30 Lafarge Process and equipment for drying solid waste material using gas from a clinker cooler

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