JP2002233732A - Waste smoke treating agent and method for producing cement by using the same - Google Patents

Waste smoke treating agent and method for producing cement by using the same

Info

Publication number
JP2002233732A
JP2002233732A JP2001145748A JP2001145748A JP2002233732A JP 2002233732 A JP2002233732 A JP 2002233732A JP 2001145748 A JP2001145748 A JP 2001145748A JP 2001145748 A JP2001145748 A JP 2001145748A JP 2002233732 A JP2002233732 A JP 2002233732A
Authority
JP
Japan
Prior art keywords
flue gas
cement
treating agent
gas treating
cao
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
JP2001145748A
Other languages
Japanese (ja)
Inventor
Yasuhiro Uchiyama
康広 内山
Junji Asaumi
順治 浅海
Takeshi Tsuzumi
毅 津々見
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.)
Taiheiyo Cement Corp
Original Assignee
Taiheiyo Cement 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 Taiheiyo Cement Corp filed Critical Taiheiyo Cement Corp
Priority to JP2001145748A priority Critical patent/JP2002233732A/en
Publication of JP2002233732A publication Critical patent/JP2002233732A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00Hydraulic cements
    • C04B7/36Manufacture of hydraulic cements in general
    • C04B7/38Preparing or treating the raw materials individually or as batches, e.g. mixing with fuel
    • C04B7/42Active ingredients added before, or during, the burning process
    • C04B7/421Inorganic materials
    • C04B7/424Oxides, Hydroxides
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/06Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
    • C04B18/062Purification products of smoke, fume or exhaust-gases
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00034Physico-chemical characteristics of the mixtures
    • C04B2111/00215Mortar or concrete mixtures defined by their oxide composition
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Abstract

PROBLEM TO BE SOLVED: To obtain a waste smoke treating agent which, when it becomes wastes, can be easily used as a cement material without carrying out a complicated calculation for proportioning raw materials and to provide a method for producing a cement by using the same as a part of the raw materials. SOLUTION: The waste smoke treating agent has a composition of 60-70 mass % CaO, 10-17 mass % SiO2, 1-5 mass % Al2O3, and 1-3 mass % Fe2O3. When the agent becomes a soot-containing one after it is used, it is washed with water and is then fed into a cement production process in the position where the temperature is in the range of 700-1,100 deg.C.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、ごみ焼却炉等の排
煙を浄化するための排煙処理剤、およびその排煙処理剤
を排煙処理に使用した後、原料の一部として用いてセメ
ントを製造する方法に関する。
The present invention relates to a flue gas treating agent for purifying flue gas from a refuse incinerator or the like, and the use of the flue gas treating agent as a part of raw materials after the flue gas treatment. The present invention relates to a method for producing cement.

【0002】[0002]

【従来の技術】排煙処理剤は、ごみ焼却等に伴って発生
する排煙中の塩化水素、硫黄酸化物等の酸性ガスやダイ
オキシン類等の有害物質を排煙から除去するための薬剤
である。排煙処理剤の主成分として、多くの場合、水酸
化カルシウムが用いられる。そして、これにダイオキシ
ンや水銀を吸着するための活性炭が添加されたものが多
い。また、ごみ焼却炉バグフィルターでの排煙の濾過性
を向上するため、珪藻土が添加されることもある。
2. Description of the Related Art A flue gas treatment agent is a chemical for removing harmful substances such as hydrogen chloride and sulfur oxides and harmful substances such as dioxins from flue gas generated by incineration of refuse. is there. Calcium hydroxide is often used as a main component of the flue gas treatment agent. Activated carbon for adsorbing dioxin and mercury is often added to this. Also, diatomaceous earth may be added in order to improve the filterability of flue gas with a garbage incinerator bag filter.

【0003】排煙処理剤は通常、排煙の煙道に乾式また
は湿式で吹き込まれ、煙道またはバグフィルター上で種
々の有害物質と反応し、排煙から有害物質を吸着・除去
する。有害物質を吸着した排煙処理剤は、バグフィルタ
ーや電気集塵機によって捕集され、使用済み排煙処理剤
としてごみ焼却プロセスから排出される。このようにし
て発生した使用済み排煙処理剤は、セメント固化、薬剤
処理、酸洗浄あるいは溶融などの方法で中間処分された
後、最終処分場に埋め立てられるが、近年最終処分場の
残余容量が逼迫しており、使用済み排煙処理剤の減量や
減容あるいは再資源化が望まれている。
[0003] The flue gas treating agent is usually blown dry or wet into the flue of the flue gas, reacts with various harmful substances on the flue or the bag filter, and adsorbs and removes harmful substances from the flue gas. The flue gas treatment agent that has adsorbed harmful substances is collected by a bag filter or an electric dust collector, and is discharged from the refuse incineration process as used smoke treatment agent. The spent flue gas treatment agent generated in this way is interim disposed by methods such as solidification of cement, chemical treatment, acid washing or melting, and is then reclaimed at the final disposal site. Due to tightness, there is a demand for the reduction and volume reduction or recycling of used flue gas treatment agents.

【0004】一方、セメントの製造工程は、高温で原料
を焼成する工程を有し、焼成工程に投入される原料が所
定の化学組成になっていれば、セメントを製造すること
ができる。このような特徴を生かし、セメント製造にお
いては、廃棄物処理に貢献するために、また、廃棄物を
原料の一部として使用することでセメント製造のコスト
ダウンも図れることから、近年、積極的に廃棄物をセメ
ント原燃料に使用されてきた。有害物質を吸着・除去し
て使用済みとなった排煙処理剤についても、前述したよ
うな社会的要請もあって、セメント製造で原料の一部と
して使用されてきた。
[0004] On the other hand, the cement manufacturing process includes a process of firing the raw material at a high temperature, and the cement can be manufactured as long as the raw material supplied to the firing process has a predetermined chemical composition. Taking advantage of these characteristics, cement manufacturing has been actively used in recent years in order to contribute to waste treatment and to reduce the cost of cement manufacturing by using waste as a part of raw materials. Waste has been used as raw material for cement. Smoke treatment agents that have become used after adsorbing and removing harmful substances have also been used as a part of raw materials in cement production due to social demands as described above.

【0005】[0005]

【発明が解決しようとする課題】しかし、使用済み排煙
処理剤は、通常、セメント原料と化学組成が大きく異な
り、また、ダイオキシン類などの有害成分や塩素分など
のセメント製造上の支障となる成分を含んでいる。その
ため使用済み排煙処理剤をセメント原料の一部に使用し
て処理する場合、複雑な原料調合計算を行うか、また
は、使用済み排煙処理剤の投入量を、セメント製造に影
響ない程度の少量に制限しなければならないとの問題が
あった。
However, the used flue gas treating agent usually has a large difference in chemical composition from the cement raw material, and also hinders the production of cement such as harmful components such as dioxins and chlorine. Contains ingredients. Therefore, when using used flue gas treating agent as a part of cement raw material, it is necessary to perform complicated raw material mixture calculation or to reduce the amount of used flue gas treating agent so that it does not affect cement production. There was a problem that it had to be limited to a small amount.

【0006】[0006]

【課題を解決するための手段】発明者らは、排煙処理剤
の成分に注目し、特定の成分の排煙処理剤を用いれば、
使用済みとなった後、容易にセメント原料として使用し
てセメントを製造できることを見出し、しかも排煙処理
剤の主成分たるCaO分がセメント製造の中間物質中に含
まれていることに着目して本発明を完成するに至った。
Means for Solving the Problems The inventors pay attention to the components of the flue gas treating agent, and if the flue gas treating agent of a specific component is used,
After being used, they found that cement can be easily used as a raw material for cement, and found that CaO, which is the main component of the flue gas treatment agent, is contained in the cement production intermediate. The present invention has been completed.

【0007】具体的には、本発明の排煙処理剤は、
(1)酸化物質量基準でCaOを60〜70%、SiO2を10〜17
%、Al2O3を1〜5%、Fe2O3を1〜3%含む排煙処理剤、ま
たは(2)酸化物質量基準でCaOを60〜70%、SiO2を10
〜17%、Al2O3を1〜5%、Fe2O3を1〜3%含む無機粉体10
0重量部と、活性炭1〜35重量部とを含む排煙処理剤であ
る。また本発明の排煙処理剤は、(3)活性炭の比表面
積が1000m2/g以上であるもの、(4)CaO分の半分以上
が遊離石灰であるものを含む。さらに本発明の排煙処理
剤は、酸化物質量基準でCaOを60〜70%、SiO2を10〜17
%、Al2O3を1〜5%、Fe2O3を1〜3%含む成分が、(5)
プレヒーターを含むセメント焼成工程のうち700〜1100
℃の温度域から抽出された焼成途中の無機粉体であるも
の、(6)プレヒーターを含むセメント焼成工程のうち
700〜1100℃の温度域から抽出された焼成途中の無機粉
体を消化して、CaO分の一部または全てを水酸化カルシ
ウムの形態にしたものを含む。また本発明は、(7)上
記排煙処理剤を排煙処理に使用し、使用済みとなった煤
塵を含む排煙処理剤を、プレヒーターを含むセメント焼
成工程のうち、700〜1100℃の温度域の位置から投入す
るセメント製造方法を含み、本発明のセメント製造方法
は、(8)該使用済み排煙処理剤を、水を用いて洗浄し
た後、セメント製造工程に投入するセメント製造方法を
含む。
Specifically, the flue gas treating agent of the present invention comprises:
(1) 60% to 70% of CaO in oxide mass basis, the SiO 2 10 to 17
%, The Al 2 O 3 1 to 5%, flue gas treatment agent containing Fe 2 O 3 1 to 3%, or (2) 60% to 70% of CaO in oxide mass basis, the SiO 2 10
To 17% Al 2 O 3 1-5%, the inorganic powder 10 containing Fe 2 O 3 1~3%
It is a flue gas treatment agent containing 0 parts by weight and 1 to 35 parts by weight of activated carbon. Further, the flue gas treatment agent of the present invention includes (3) one in which the specific surface area of activated carbon is 1000 m 2 / g or more, and (4) one in which half or more of CaO is free lime. Further, the flue gas treating agent of the present invention contains 60 to 70% of CaO and 10 to 17% of SiO 2 based on the mass of the oxide.
%, 1 to 5% of Al 2 O 3, and a component containing 1 to 3% of Fe 2 O 3 are (5)
700 to 1100 of cement firing process including pre-heater
(6) Cement firing process including a preheater, which is an inorganic powder during firing extracted from the temperature range of ℃.
Includes those obtained by digesting inorganic powder during calcination extracted from the temperature range of 700 to 1100 ° C. and converting part or all of CaO to calcium hydroxide. Further, the present invention provides (7) using the above-mentioned flue gas treating agent for flue gas treatment, and converting the flue gas treating agent containing used dust to 700 to 1100 ° C. in a cement firing step including a pre-heater. The cement manufacturing method of the present invention includes a cement manufacturing method of charging from a position in a temperature range, and (8) a cement manufacturing method of cleaning the used flue gas treating agent using water and then inputting it to a cement manufacturing process. including.

【0008】[0008]

【発明の実施の形態】本発明の排煙処理剤は、酸化物質
量基準でCaOを60〜70%、SiO2を10〜17%、Al2O3を1〜5
%、Fe2O3を1〜3%含むことを特徴とする。CaO、SiO2
Al2O3、Fe2O3は、セメントクリンカの主成分である。セ
メント製造においては、石灰石、粘土、鉄原料等が、酸
化物質量基準でCaOが60〜70%、SiO2が10〜17%、Al2O3
が1〜5%、Fe2O3が1〜3%の範囲内になるように粉砕・
混合され、セメント焼成炉へ供給される。焼成炉内で
は、CaO、SiO2、Al2O3、Fe2O 3を含む混合物に、ロータ
リーキルンのバーナーへと供給される燃料中の灰分が加
わり、セメントクリンカを形成するために最適な成分組
成となる。本発明では、排煙処理剤の組成を、酸化物質
量基準でCaOが60〜70%、SiO2が10〜17%、Al2O3が1〜5
%、Fe2O3が1〜3%の範囲とする。これは、セメント製
造工程で石灰石、粘土、鉄原料等が粉砕・混合されて焼
成炉へ供給される際の組成に近いものであり、これによ
り、排煙処理剤にごみ焼却等の煤塵が加わって使用済み
となった際、セメントクリンカを形成するのに好適な成
分組成になるという効果を奏する。しかも、排煙処理剤
として排煙中の有害物質を吸収する性能についても、従
来の排煙処理剤と同等のものが得られる。組成がこの範
囲から外れると、排煙処理に使用した後の組成がセメン
ト用原料として適した範囲から外れることがある。その
ため、セメント原料に使用するときに再度組成の調整が
必要となるので好ましくない。該排煙処理剤中のCaO、S
iO2、Al2O3、Fe2O3の各成分が、本発明の範囲内にあれ
ば、それ以外の成分はセメント製造に支障のない限り何
を用いても構わず、ダイオキシン類を吸着・除去するた
めの活性炭を混合し、または併用することもできる。ま
た、バグフィルターでの排煙の濾過性を向上するため、
珪藻土を添加しても良い。
DETAILED DESCRIPTION OF THE INVENTION The flue gas treating agent of the present invention is an oxidizing substance.
60-70% CaO, SiOTwo10 ~ 17%, AlTwoOThree1 to 5
%, FeTwoOThree1 to 3%. CaO, SiOTwo,
AlTwoOThree, FeTwoOThreeIs the main component of cement clinker. C
In the production of cement, limestone, clay, iron raw materials, etc.
60-70% of CaO, SiOTwoIs 10-17%, AlTwoOThree
1-5%, FeTwoOThreeCrushed so that is within the range of 1-3%
It is mixed and supplied to a cement firing furnace. In the firing furnace
Is CaO, SiOTwo, AlTwoOThree, FeTwoO ThreeThe mixture containing
The ash content in the fuel supplied to the
In addition, the optimal component set for forming the cement clinker
Will be successful. In the present invention, the composition of the flue gas treatment agent is
60-70% CaO, SiOTwoIs 10-17%, AlTwoOThreeIs 1 to 5
%, FeTwoOThreeIs in the range of 1 to 3%. It is made of cement
Limestone, clay, iron raw materials, etc. are ground and mixed during the
It is close to the composition when supplied to the furnace,
Used as a result of the addition of dust from incineration
When it becomes, the composition suitable for forming the cement clinker
It has the effect of becoming a minute composition. Moreover, the flue gas treatment agent
As for the performance of absorbing harmful substances in flue gas,
The equivalent of conventional flue gas treatment agents is obtained. Composition is in this range
If it is out of the surroundings, the composition after using it for smoke
May be out of the range suitable as a raw material for That
Therefore, when used as a cement raw material, the composition must be adjusted again.
It is not preferable because it becomes necessary. CaO, S in the flue gas treatment agent
iOTwo, AlTwoOThree, FeTwoOThreeAre within the scope of the present invention.
If the other components do not interfere with cement production,
Can be used to adsorb and remove dioxins.
Activated carbon can be mixed or used in combination. Ma
In addition, in order to improve the filterability of smoke exhaust with a bag filter,
Diatomaceous earth may be added.

【0009】活性炭を使用する場合には、酸化物質量基
準でCaOを60〜70%、SiO2を10〜17%、Al2O3を1〜5%、
Fe2O3を1〜3%含む無機粉体100重量部に対し、活性炭1
〜35重量部を添加することが好ましい。活性炭が1重量
部に満たない時は、排煙中のダイオキシン類を十分に吸
着できない。活性炭が多すぎる場合には、排煙処理剤の
投入量が増え、使用後の排煙処理剤の処理量も増加する
ため不経済である。また、活性炭量が増えると、後述の
使用済み排煙処理剤の水洗処理において、濾過工程に支
障をきたすおそれがあるため好ましくない。活性炭の比
表面積を1000m2/g以上とすれば、ダイオキシン類の吸着
効率が高く、排煙処理剤中の活性炭量を1〜15質量%に
抑えることが可能であり、後述の使用済み排煙処理剤の
水洗処理において、濾過工程が効率化されるため、特に
好ましい。また、活性炭の種類は特に限定されず、植物
系、鉱物系いずれのものでも良い。
[0009] When using activated carbon, 60% to 70% of CaO in oxide mass basis, the SiO 2 10~17%, Al 2 O 3 1-5%,
Activated carbon 1 per 100 parts by weight of inorganic powder containing 1-3% Fe 2 O 3
It is preferred to add up to 35 parts by weight. If the amount of activated carbon is less than 1 part by weight, dioxins in the flue gas cannot be sufficiently adsorbed. If the amount of activated carbon is too large, it is uneconomical because the amount of the flue gas treating agent increases and the amount of the used flue gas treating agent increases. In addition, an increase in the amount of activated carbon is not preferable because the filtration step may be hindered in the washing treatment of the used flue gas treating agent described below. If the specific surface area of the activated carbon is 1000 m 2 / g or more, the adsorption efficiency of dioxins is high, and the amount of activated carbon in the flue gas treatment agent can be suppressed to 1 to 15% by mass. In the water washing treatment of the treating agent, the filtering step is more efficient, which is particularly preferable. The type of activated carbon is not particularly limited, and may be any of plant-based and mineral-based.

【0010】本発明の排煙処理剤中のCaOは、遊離石
灰、すなわち水酸化カルシウムまたは酸化カルシウムの
形態であれば、排煙中の有害物質(塩化水素、硫黄酸化
物等の酸性ガス)との反応性が高い。したがって、本発
明の排煙処理剤中のCaOは、少なくともその半分以上が
水酸化カルシウムまたは酸化カルシウムの形態、または
それらの混合物であることが好ましい。
[0010] CaO in the flue gas treatment agent of the present invention, if it is in the form of free lime, ie, calcium hydroxide or calcium oxide, is mixed with harmful substances (acid gas such as hydrogen chloride and sulfur oxide) in the flue gas. High reactivity. Therefore, it is preferable that at least half or more of CaO in the flue gas treatment agent of the present invention is in the form of calcium hydroxide or calcium oxide, or a mixture thereof.

【0011】本発明の排煙処理剤のうち、酸化物質量基
準でCaOを60〜70%、SiO2を10〜17%、Al2O3を1〜5%、
Fe2O3を1〜3%含む成分として、プレヒーターを含むセ
メント焼成工程のうち700〜1100℃の温度域から抽出さ
れた焼成途中の無機粉体を用いることができる。セメン
ト製造工程のうちでもプレヒーターを含むセメント焼成
工程のうち、700〜1100℃の温度域から抽出された成分
は、酸化物質量基準での成分組成が発明の範囲内であ
り、使用済みとなった後、成分調整をすることなくセメ
ント原料に用いることができるばかりでなく、CaO分
が、塩化水素や硫黄酸化物との反応性の高い酸化カルシ
ウムの形態となっており、排煙処理剤として好適であ
る。また、SiO2、Al2O3、Fe2O3の各成分が、バグフィル
ターでの排煙の濾過助材としての機能を有しており、排
煙処理剤としてさらに好適である。抽出する箇所の温度
域が700℃未満では、CaO分の一部が、排煙処理剤として
の活性が十分でない炭酸カルシウムの形態になるため好
ましくない。一方、セメント製造工程のうち温度域が11
00℃を越える位置はロータリーキルンであり、ロータリ
ーキルンから焼成途中の無機粉体を抽出するのは装置上
困難である。また、仮に抽出したとしても、焼成が進ん
で遊離石灰の形態でのCaO分がほとんど得られず、排煙
処理剤として不適である。該排煙処理剤の成分を抽出す
る位置は、例えば、プレヒーターの最下段サイクロンの
下部があげられる。抽出は、一例をあげれば、抽出位置
に開口部を設け、開口部に粉体搬送装置、例えばスクリ
ューコンベア、あるいは外付けの吸引ポンプで吸引でき
る仕組みを備えたチューブなどを挿入し、落下してくる
セメント中間生成物を粉体搬送装置で受けてセメント製
造系外に搬出するなどの方法で行なえばよい。抽出直
後、抽出物を外気に曝すと抽出物中の酸化カルシウムが
空気中の炭酸ガスや水分と反応して排煙処理剤としての
活性が低下するおそれがあるため、抽出装置を、外気を
遮断できる構造とするなどの対策を施すことが好まし
い。
[0011] Of the flue gas treatment agent of the present invention, 60% to 70% of CaO in oxide mass basis, the SiO 2 10~17%, Al 2 O 3 1-5%,
As the component containing 1 to 3% of Fe 2 O 3 , inorganic powder in the middle of firing extracted from a temperature range of 700 to 1100 ° C. in a cement firing step including a preheater can be used. The components extracted from the temperature range of 700 to 1100 ° C in the cement firing process including the pre-heater in the cement manufacturing process have a component composition on an oxide mass basis within the scope of the invention and have been used. After that, not only can it be used as a cement raw material without adjusting the components, but also CaO is in the form of calcium oxide, which is highly reactive with hydrogen chloride and sulfur oxides, It is suitable. Further, each component of SiO 2 , Al 2 O 3 , and Fe 2 O 3 has a function as a filter aid for flue gas with a bag filter, and is more suitable as a flue gas treatment agent. If the temperature range of the extraction point is lower than 700 ° C., a part of the CaO content is not preferable because it has a form of calcium carbonate having insufficient activity as a smoke exhaust treatment agent. On the other hand, the temperature range of the cement manufacturing process was 11
The position exceeding 00 ° C. is a rotary kiln, and it is difficult to extract inorganic powder during firing from the rotary kiln on an apparatus. Even if it is extracted, the calcination proceeds and almost no CaO content in the form of free lime is obtained, which is unsuitable as a flue gas treatment agent. The position where the components of the smoke exhausting agent are extracted is, for example, the lower part of the lowermost cyclone of the preheater. For the extraction, for example, an opening is provided at the extraction position, and a powder conveying device, for example, a screw conveyor, or a tube equipped with a mechanism that can be suctioned by an external suction pump is inserted into the opening, and then dropped. It may be carried out by a method such as receiving the incoming cement intermediate product with a powder conveying device and carrying it out of the cement production system. Immediately after the extraction, if the extract is exposed to the outside air, the calcium oxide in the extract may react with carbon dioxide and water in the air and reduce the activity as a flue gas treatment agent. It is preferable to take countermeasures such as adopting a structure that can be used.

【0012】該抽出物中の酸化カルシウムの一部または
全てを消化して、水酸化カルシウムの形態にしても良
い。消化の方法は、炭酸化による活性の低下を防ぎなが
ら、水分と反応させるものであれば特に限定されない。
水酸化カルシウムの比表面積を大きくするために、消化
反応遅延剤としてアルコール等の有機溶剤を消化水に添
加するなどの種々の消化方法が提案されており、これら
の従来法から選択することができる。
Some or all of the calcium oxide in the extract may be digested to form calcium hydroxide. The digestion method is not particularly limited as long as it reacts with moisture while preventing a decrease in activity due to carbonation.
In order to increase the specific surface area of calcium hydroxide, various digestion methods such as adding an organic solvent such as alcohol to digestion water as a digestion reaction retarder have been proposed, and can be selected from these conventional methods. .

【0013】本発明の排煙処理剤は、ごみ焼却場等にお
いて従来の排煙処理剤の吹き込み装置をそのまま用いて
吹き込むことができる。該排煙処理剤の煙道への吹き込
み量は、多いほど有害物質の吸着量が多く、排煙の浄化
効果が高いが、吹き込み量が多すぎれば、浄化効果の割
に余計な排煙処理剤を吹き込むことになり不経済とな
る。したがって、該排煙処理剤の吹き込み量は、ごみ焼
却によって発生する排煙の成分組成にもよるが、概ね排
煙中の煤塵量の等量〜10倍程度が好ましい。
The flue gas treating agent of the present invention can be blown in a refuse incineration plant or the like by using a conventional flue gas treating agent blowing device as it is. The greater the amount of the smoke treatment agent blown into the flue, the greater the amount of harmful substances adsorbed and the higher the effect of purifying the smoke. It is uneconomical to inject the agent. Therefore, the blowing amount of the flue gas treating agent depends on the component composition of the flue gas generated by the incineration of the refuse, but is preferably about equivalent to about 10 times the amount of the dust in the flue gas.

【0014】本発明のセメント製造方法は、上記排煙処
理剤を排煙処理に使用し、使用済みとなった煤塵を含む
排煙処理剤を、プレヒーターを含むセメント焼成工程の
うち、700〜1100℃の温度域の位置から投入するセメン
ト製造方法である。使用済みとなった排煙処理剤は、セ
メント製造工程において調合原料に混合し、調合原料と
ともにセメント焼成炉へと投入することができる。しか
し、近年、排煙とともに排出されるダイオキシン類の量
が規制され、そのため活性炭を混合した排煙処理剤を用
いてダイオキシン類を排煙から吸着除去する技術が用い
られるようになった。このような方法による排煙処理剤
は、ダイオキシン類を含有しており、そのため、調合原
料とともにセメント焼成炉へと投入すると、焼成炉上流
部(プレヒーター)の比較的低温(200〜400℃)の位置
でダイオキシン類が揮発し、セメント製造設備からダイ
オキシンが排出されてしまう懸念がある。廃棄物を再資
源化する上で、ダイオキシン類を発生させてはならない
ことは周知である。本発明では、プレヒーターを含むセ
メント焼成工程のうち、700〜1100℃の位置に使用済み
排煙処理剤を投入する。使用済み排煙処理剤とともに投
入されたダイオキシン類は直ちに700〜1100℃の高温に
さらされ、さらに高温のロータリーキルンへと導かれる
ため、瞬時に分解する。したがって、二次的な汚染を発
生することなく、使用済み排煙処理剤を用いてセメント
を製造することができる。投入する箇所の温度が700℃
未満では、排煙処理剤から揮発したダイオキシンが完全
には分解されない可能性があるため好ましくない。一
方、セメント焼成工程のうち温度が1100℃を越える位置
はロータリーキルン内部であり、ロータリーキルンの途
中に排煙処理剤の投入口を設けるのは装置上困難であ
る。本発明は、使用済みとなった排煙処理剤がセメント
製造に好適な組成であることを利用する。そのため原料
調合の際に組成の調整は必要ではなく、原則としてその
ままセメント焼成工程に投入することができる。さら
に、従来の使用済排煙処理剤よりも投入量を格段に大き
くすることができるという利点を有する。使用済み排煙
処理剤の投入位置は、例えば、仮焼炉、ロータリーキル
ン入口(窯尻)などがあげられる。それらの位置に二重
ダンパーを備えた開口部を設け、適当な粉体搬送装置、
例えばスクリューコンベア、ポンプ等を用いて使用済み
排煙処理剤を投入すればよい。
[0014] In the cement production method of the present invention, the above-mentioned flue gas treating agent is used for flue gas treatment, and the spent flue gas treating agent containing soot and dust is used in a cement firing step including a pre-heater in a cement sintering step. This is a method for producing cement that is charged from a temperature range of 1100 ° C. The used flue gas treating agent can be mixed with the blended raw material in the cement manufacturing process, and can be put into the cement firing furnace together with the blended raw material. However, in recent years, the amount of dioxins discharged together with flue gas has been regulated, and therefore, a technique of adsorbing and removing dioxins from flue gas using a flue gas treating agent mixed with activated carbon has been used. The flue gas treatment agent obtained by such a method contains dioxins, and therefore, when put into a cement firing furnace together with the prepared raw materials, a relatively low temperature (200 to 400 ° C.) of the upstream portion of the firing furnace (preheater) is used. There is a concern that dioxins will be volatilized at the position of and the dioxin will be discharged from the cement production facility. It is well known that dioxins must not be generated in recycling waste. In the present invention, in the cement firing step including the preheater, the used flue gas treating agent is charged at a position of 700 to 1100 ° C. The dioxins charged together with the used flue gas treatment agent are immediately exposed to a high temperature of 700 to 1100 ° C, and are guided to a high-temperature rotary kiln, where they are instantaneously decomposed. Therefore, cement can be manufactured using the used flue gas treating agent without generating secondary pollution. The temperature at the point of introduction is 700 ° C
If it is less than 1, the dioxin volatilized from the flue gas treating agent may not be completely decomposed, which is not preferable. On the other hand, the position in the cement firing step where the temperature exceeds 1100 ° C. is inside the rotary kiln, and it is difficult to provide an inlet for the flue gas treating agent in the middle of the rotary kiln. The present invention utilizes the fact that the spent flue gas treating agent has a composition suitable for cement production. Therefore, it is not necessary to adjust the composition at the time of mixing the raw materials, and in principle, it can be directly input to the cement firing step. Further, there is an advantage that the input amount can be remarkably increased as compared with the conventional used flue gas treating agent. The charging position of the used flue gas treating agent is, for example, a calciner, a rotary kiln inlet (kiln bottom), or the like. Provide openings with double dampers at those positions, suitable powder conveying device,
For example, the used flue gas treatment agent may be charged using a screw conveyor, a pump, or the like.

【0015】本発明のセメント製造方法は、該使用済み
排煙処理剤を、水を用いて洗浄した後、セメント製造工
程に投入するセメント製造方法を含む。使用済み排煙処
理剤には、前述のようにダイオキシン類が含まれる場合
がある他、塩素分を含んでいる。塩素がセメントに残留
すれば、鉄筋の錆などの原因となるため好ましくない。
また、塩素分はセメント焼成炉内で揮発しやすい化合物
を生成する。これらの化合物は、ロータリーキルン内で
揮発してプレヒーターに凝縮し、固結となって、時には
プレヒーターの詰まりなどを引き起こしてセメント製造
上の支障となる。そのため使用済み排煙処理剤のセメン
ト原料としての使用量が制限されることがある。本発明
では、あらかじめ使用済み排煙処理剤を水で洗浄するこ
とで、セメント製造上の支障となる塩素分を除去するこ
とができ、セメント製造上の支障をきたすことがなく、
多量の使用済み排煙処理剤をセメント製造に用いること
ができる。水洗方法は、例えば、適当な溶解槽に水を入
れ、使用済み排煙処理剤を加えて撹拌し、懸濁液をフィ
ルタープレス、ベルトフィルター等で濾過、脱水するな
どの方法で行なえばよく、得られた脱水ケーキをセメン
ト原料として使用する。なお、濾液は排煙処理剤中のカ
ルシウム分の影響でアルカリ性となっているので中和処
理し、中和により生じた沈澱を除去し、溶存重金属等を
除去するなど廃水処理した後、排水すればよい。
[0015] The cement production method of the present invention includes a cement production method in which the used flue gas treating agent is washed with water and then put into a cement production step. The used flue gas treatment agent may contain dioxins as described above, and also contains chlorine. If chlorine remains in the cement, it may cause rust on the reinforcing steel bars, which is not preferable.
Further, the chlorine component generates a compound which is easily volatilized in the cement firing furnace. These compounds volatilize in the rotary kiln and condense on the pre-heater and solidify, sometimes causing clogging of the pre-heater, which hinders the production of cement. Therefore, the amount of the used flue gas treating agent as a cement raw material may be limited. In the present invention, by washing the used flue gas treating agent with water in advance, it is possible to remove chlorine that hinders cement production, and does not hinder cement production.
Large amounts of used flue gas treatment agents can be used for cement production. The water washing method may be performed by, for example, putting water in an appropriate dissolving tank, adding a used flue gas treating agent and stirring, filtering the suspension with a filter press, a belt filter, etc., and dehydrating the suspension. The obtained dehydrated cake is used as a cement raw material. Since the filtrate is alkaline due to the calcium content in the flue gas treatment agent, it is neutralized, the precipitate generated by the neutralization is removed, the wastewater is removed by removing dissolved heavy metals, etc., and then the wastewater is drained. I just need.

【0016】[0016]

【実施例】以下、実施例により本発明について説明す
る。 (実施例1)セメント焼成工程のうち、プレヒーターの
最もロータリーキルン寄りにあるサイクロンの下部よ
り、焼成途中の粉体を抽出し排煙処理剤を得た。抽出位
置の温度は、1000℃であった。抽出した排煙処理剤の成
分を蛍光X線分析装置により分析した結果、酸化物質量
としてCaOが65%、SiO2が14%、Al2O3が3.5%、Fe2O3
1.5%含まれていた。この粉体0.5gを燃焼ボートに量り
取り、内径3cmのほう珪酸ガラス製反応管中に置き、管
状炉で200℃に加熱しながら、水分20%、HClを2000ppm
含む窒素ガスを流速0.5m/minで3時間流し、該排煙処理
剤にHClガスを吸収させた。該排煙処理剤のHCl吸収量
は、該排煙処理剤中のCaOの1gあたり0.13gと市販の排煙
処理剤と同等の性能であった。次に、該排煙処理剤と活
性炭(比表面積1050 m2/g)を質量割合で9:1に混合
し、ごみ焼却炉のバグフィルター直前より、煤塵質量の
約5倍量を吹き込み、煤塵と該排煙処理剤をバグフィル
ターにて捕集し、使用済み排煙処理剤を得た。得られた
使用済み排煙処理剤の成分を表1に示す。この使用済み
排煙処理剤を、セメント焼成炉の温度1000℃の位置か
ら、セメントクリンカ製造量1tあたり120kg分投入し、
それ以外は通常どおりの工程でセメントを製造したが、
セメント焼成炉排ガス中からダイオキシン類は検出され
ず、得られたクリンカも、表1に示す通り通常のクリン
カと全く同等の品質であった。
The present invention will be described below with reference to examples. (Example 1) In the cement firing step, the powder during firing was extracted from the lower part of the cyclone closest to the rotary kiln of the preheater to obtain a flue gas treating agent. The temperature at the extraction position was 1000 ° C. Extracted flue gas treatment agent was analyzed by component a fluorescent X-ray analyzer, CaO 65% as an oxide mass, SiO 2 is 14% Al 2 O 3 is 3.5%, the Fe 2 O 3
1.5% was included. 0.5 g of this powder is weighed into a combustion boat, placed in a borosilicate glass reaction tube having an inner diameter of 3 cm, and heated to 200 ° C. in a tubular furnace, while containing 20% of water and 2,000 ppm of HCl.
Nitrogen gas was flowed at a flow rate of 0.5 m / min for 3 hours to allow the flue gas treatment agent to absorb HCl gas. The amount of HCl absorbed by the flue gas treating agent was 0.13 g per 1 g of CaO in the flue gas treating agent, which was equivalent to that of a commercially available flue gas treating agent. Next, the flue gas treatment agent and activated carbon (specific surface area 1050 m 2 / g) were mixed in a mass ratio of 9: 1, and immediately before the bag filter of the refuse incinerator, about 5 times the mass of the dust was blown. And the flue gas treating agent were collected by a bag filter to obtain a used flue gas treating agent. Table 1 shows the components of the obtained used flue gas treating agent. This spent flue gas treatment agent is put into the cement baking furnace at a temperature of 1000 ° C from the position of 120 kg per 1 t of cement clinker production,
Other than that, cement was manufactured in the usual process,
Dioxins were not detected in the exhaust gas from the cement sintering furnace, and the obtained clinker was of exactly the same quality as a normal clinker as shown in Table 1.

【0017】(実施例2)実施例1と同様にして得た排
煙処理剤に、実施例1と同様に活性炭を混合した後、塩
素分の多いごみを焼却中のごみ焼却炉のバグフィルター
直前より、煤塵質量の約5倍量を吹き込み、煤塵と該排
煙処理剤をバグフィルターにて捕集し、使用済み排煙処
理剤を得た。得られた使用済み排煙処理剤の成分を表1
に示す。この使用済み排煙処理剤1kgあたり10Lの水を加
えて撹拌した後、フィルタープレスを用いて濾過し、脱
水ケーキを得た。水洗後の成分(乾燥状態)を表1に示
す。この脱水ケーキを乾燥した後、セメント焼成炉の温
度1000℃の位置から、セメントクリンカ製造量1tあたり
120kg分投入し、それ以外は通常どおりの工程でセメン
トを製造したが、セメント焼成炉排ガス中からダイオキ
シン類は検出されず、得られたクリンカも、表1に示す
通り通常のクリンカと全く同等の品質であった。
(Example 2) A bag filter of a refuse incinerator in which garbage containing a large amount of chlorine is being incinerated after mixing activated carbon with the flue gas treating agent obtained in the same manner as in Example 1 Immediately before, about 5 times the mass of the dust was blown, and the dust and the smoke-treating agent were collected by a bag filter to obtain a used smoke-treating agent. Table 1 shows the components of the obtained used flue gas treating agent.
Shown in After adding and stirring 10 L of water per 1 kg of the used flue gas treating agent, the mixture was filtered using a filter press to obtain a dehydrated cake. Table 1 shows the components (dry state) after washing with water. After drying this dewatered cake, the cement baking furnace temperature from 1000 ° C
The cement was manufactured in the usual process except that it was charged for 120 kg, but dioxins were not detected in the exhaust gas from the cement firing furnace, and the obtained clinker was completely equivalent to the normal clinker as shown in Table 1. It was quality.

【0018】(比較例)市販の排煙処理剤(JIS R 9001
特号消石灰)を、実施例1と同様に0.5gを燃焼ボートに
量り取り、内径3cmのほう珪酸ガラス製反応管中に置
き、管状炉で200℃に加熱しながら、水分20%、HClを20
00ppm含む窒素ガスを流速0.5m/minで流し、該排煙処理
剤にHClガスを吸収させた。該排煙処理剤のHCl吸収量
は、該排煙処理剤中のCaOの1gあたり0.14gであった。つ
ぎに、市販の排煙処理剤(JIS R 9001特号消石灰)に、
実施例1と同様に活性炭を混合した後、焼却中のごみ焼
却炉のバグフィルター直前より、煤塵質量の約5倍量を
吹き込み、煤塵と該排煙処理剤をバグフィルターにて捕
集し、使用済み排煙処理剤を得た。得られた使用済み排
煙処理剤の成分を表1に示す。この使用済み排煙処理剤
を、セメント焼成炉の温度1000℃の位置から投入し、そ
れ以外は通常どおりの工程でセメントを製造した。得ら
れたセメントの品質は、使用済み排煙処理剤の投入量が
セメントクリンカ製造量1tあたり30kgでは、通常のセメ
ントと全く同等であった。しかし、投入量をセメントク
リンカ製造量1tあたり60kgとしたところ、表1に示す通
り、クリンカ中の遊離石灰分が1.3%となり、不良品と
なった。したがって、この比較例の使用済み排煙処理剤
をセメント原料に用いる場合、投入量は最大でもセメン
トクリンカ製造量1tあたり60kg未満でなければならず、
これは実施例1および2の場合の投入量(1tあたり120k
g)よりもかなり少量であった。
(Comparative Example) A commercially available flue gas treating agent (JIS R 9001)
0.5 g of special lime (lime) was weighed into a combustion boat in the same manner as in Example 1, placed in a borosilicate glass reaction tube having an inner diameter of 3 cm, and heated to 200 ° C. in a tubular furnace to remove 20% of water and HCl. 20
Nitrogen gas containing 00 ppm was flowed at a flow rate of 0.5 m / min, and the flue gas treatment agent absorbed HCl gas. The amount of HCl absorbed by the flue gas treating agent was 0.14 g per 1 g of CaO in the flue gas treating agent. Next, a commercially available flue gas treatment agent (JIS R 9001 special lime slaked)
After mixing activated carbon in the same manner as in Example 1, about 5 times the mass of the dust was blown from immediately before the bag filter of the refuse incinerator during incineration, and the dust and the flue gas treatment agent were collected by the bag filter. A used flue gas treating agent was obtained. Table 1 shows the components of the obtained used flue gas treating agent. This spent flue gas treating agent was charged at a temperature of 1000 ° C. in a cement sintering furnace, and the cement was manufactured in the usual process except for the above. The quality of the obtained cement was completely equivalent to that of ordinary cement when the used flue gas treatment agent was used in an amount of 30 kg per 1 t of cement clinker production. However, when the input amount was set to 60 kg per 1 t of cement clinker production, as shown in Table 1, the free lime content in the clinker was 1.3%, which was a defective product. Therefore, when the used flue gas treatment agent of this comparative example is used as a cement raw material, the input amount must be less than 60 kg per 1 t of cement clinker production amount at the maximum.
This is the input amount in the case of Examples 1 and 2 (120 k
It was considerably smaller than g).

【0019】[0019]

【表1】 [Table 1]

【0020】[0020]

【発明の効果】本発明によれば、複雑な調合計算をする
ことなく、従来の排煙処理剤を用いた場合に比べ各段に
大量の使用済み排煙処理剤を原料の一部に用いてセメン
トを製造することができ、セメント製造の省力化を達成
しつつ、廃棄物の一層の減量にも貢献することができ
る。さらに、多量の使用済排煙処理剤を原料の一部とし
て使用するため、セメント製造のコスト低減にも有効で
ある。
According to the present invention, a large amount of used flue gas treating agent is used for a part of the raw material in each stage as compared with the case of using the conventional flue gas treating agent without complicated formulation calculation. Cement can be produced by the method, and it is possible to contribute to further reduction of waste while achieving labor saving in cement production. Furthermore, since a large amount of used flue gas treating agent is used as a part of the raw material, it is also effective in reducing the cost of cement production.

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 20/10 B01D 53/34 134A 20/20 ZAB B09B 3/00 134E C04B 7/24 124Z 7/38 B09B 3/00 303B 7/44 303L 304Z 304G Fターム(参考) 4D002 AA02 AA19 AA21 AB01 AC04 BA03 BA04 BA14 CA01 CA11 DA05 DA11 DA12 DA16 DA22 DA41 DA46 EA13 FA02 GA01 GB08 GB12 HA01 HA04 4D004 AA37 AA50 BA10 CA30 CB09 DA03 DA06 4G012 KA08 4G066 AA05B AA14D AA17B AA20B AA22B AA27B AA43B AA75A CA07 CA31 CA33 DA02 FA11 FA22 FA34 FA37 Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) B01J 20/10 B01D 53/34 134A 20/20 ZAB B09B 3/00 134E C04B 7/24 124Z 7/38 B09B 3/00 303B 7/44 303L 304Z 304G F-term (Reference) 4D002 AA02 AA19 AA21 AB01 AC04 BA03 BA04 BA14 CA01 CA11 DA05 DA11 DA12 DA16 DA22 DA41 DA46 EA13 FA02 GA01 GB08 GB12 HA01 HA04 4D004 AA37 AA50 BA10 CA30 CB09 A03A06 4 AA17B AA20B AA22B AA27B AA43B AA75A CA07 CA31 CA33 DA02 FA11 FA22 FA34 FA37

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 酸化物質量基準でCaOを60〜70%、SiO2
を10〜17%、Al2O3を1〜5%、Fe2O3を1〜3%含む排煙処
理剤。
(1) 60 to 70% of CaO, SiO 2
The 10 to 17%, the Al 2 O 3 1 to 5% flue gas treatment agent comprising Fe 2 O 3 1~3%.
【請求項2】 酸化物質量基準でCaOを60〜70%、SiO2
を10〜17%、Al2O3を1〜5%、Fe2O3を1〜3%含む無機粉
体100重量部と、活性炭1〜35重量部とを含む排煙処理
剤。
2. 60% to 70% of CaO, SiO 2
Flue gas treating agent containing 10 to 17%, the Al 2 O 3 1 to 5% and the inorganic powder 100 parts by weight containing Fe 2 O 3 1 to 3 percent, and activated carbon 1-35 parts by weight.
【請求項3】 活性炭の比表面積が1000m2/g以上である
請求項2記載の排煙処理剤。
3. The flue gas treating agent according to claim 2 , wherein the specific surface area of the activated carbon is 1000 m 2 / g or more.
【請求項4】 請求項1〜3のいずれかに記載の排煙処
理剤のうち、CaO分の半分以上が遊離石灰である排煙処
理剤。
4. A flue gas treating agent according to claim 1, wherein at least half of CaO is free lime.
【請求項5】 酸化物質量基準でCaOを60〜70%、SiO2
を10〜17%、Al2O3を1〜5%、Fe2O3を1〜3%含む成分
が、プレヒーターを含むセメント焼成工程のうち700〜1
100℃の温度域から抽出された焼成途中の無機粉体であ
る請求項1〜4のいずれかに記載の排煙処理剤。
5. CaO content of 60 to 70% based on oxide mass, SiO 2
The 10 to 17%, the Al 2 O 3 1 to 5% is component comprising Fe 2 O 3 1 to 3% of the cement burning process including preheater 700-1
The flue gas treating agent according to any one of claims 1 to 4, wherein the inorganic powder is a calcined inorganic powder extracted from a temperature range of 100 ° C.
【請求項6】 酸化物質量基準でCaOを60〜70%、SiO2
を10〜17%、Al2O3を1〜5%、Fe2O3を1〜3%含む成分
が、プレヒーターを含むセメント焼成工程のうち700〜1
100℃の温度域から抽出された焼成途中の無機粉体を消
化して、CaO分の一部または全てを水酸化カルシウムの
形態にしたものである請求項1〜4のいずれかに記載の
排煙処理剤。
6. 60-70% of CaO based on oxide mass, SiO 2
The 10 to 17%, the Al 2 O 3 1 to 5% is component comprising Fe 2 O 3 1 to 3% of the cement burning process including preheater 700-1
The waste powder according to any one of claims 1 to 4, wherein the inorganic powder in the course of firing extracted from the temperature range of 100 ° C is digested to convert a part or all of the CaO content into a form of calcium hydroxide. Smoke treatment agent.
【請求項7】 請求項1〜6のいずれかに記載の排煙処
理剤を排煙処理に使用し、使用済みとなった煤塵を含む
排煙処理剤を、プレヒーターを含むセメント焼成工程の
うち、700〜1100℃の温度域の位置から投入するセメン
ト製造方法。
7. A method according to any one of claims 1 to 6, wherein the flue gas treating agent is used for flue gas treatment, and the spent flue gas treating agent containing dust is used in a cement firing step including a preheater. Among them, the cement production method which is charged from a position in the temperature range of 700 to 1100 ° C.
【請求項8】 使用済み排煙処理剤を、水を用いて洗浄
した後、セメント製造工程に投入する請求項7記載のセ
メント製造方法。
8. The cement production method according to claim 7, wherein the used flue gas treating agent is washed with water and then put into a cement production step.
JP2001145748A 2000-12-08 2001-05-16 Waste smoke treating agent and method for producing cement by using the same Pending JP2002233732A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP2000-374162 2000-12-08
JP2000374162 2000-12-08
JP2001145748A JP2002233732A (en) 2000-12-08 2001-05-16 Waste smoke treating agent and method for producing cement by using the same

Publications (1)

Publication Number Publication Date
JP2002233732A true JP2002233732A (en) 2002-08-20

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Country Link
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JP2007008767A (en) * 2005-06-30 2007-01-18 Mitsubishi Materials Corp Method of reducing organic chlorine compound in waste gas in cement production equipment and cement production equipment
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WO2006059718A1 (en) * 2004-12-03 2006-06-08 Mitsubishi Materials Corporation Cement clinker and process for producing the same
US7998270B2 (en) 2004-12-03 2011-08-16 Mitsubishi Materials Corporation Cement clinker and process for producing the same
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