JPS60156531A - Method of desulfurizing flue gas from combustion apparatus - Google Patents

Method of desulfurizing flue gas from combustion apparatus

Info

Publication number
JPS60156531A
JPS60156531A JP60000256A JP25685A JPS60156531A JP S60156531 A JPS60156531 A JP S60156531A JP 60000256 A JP60000256 A JP 60000256A JP 25685 A JP25685 A JP 25685A JP S60156531 A JPS60156531 A JP S60156531A
Authority
JP
Japan
Prior art keywords
flue gas
powder
gas stream
cement
hot
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
JP60000256A
Other languages
Japanese (ja)
Inventor
アルブレヒト・ウオルテル
ホルスト・ヘルヒエンバツハ
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.)
Kloeckner Humboldt Deutz AG
Original Assignee
Kloeckner Humboldt Deutz AG
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 Kloeckner Humboldt Deutz AG filed Critical Kloeckner Humboldt Deutz AG
Publication of JPS60156531A publication Critical patent/JPS60156531A/en
Pending legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/46Sulfates
    • C01F11/464Sulfates of Ca from gases containing sulfur oxides
    • 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
    • C04B11/00Calcium sulfate cements
    • C04B11/26Calcium sulfate cements strating from chemical gypsum; starting from phosphogypsum or from waste, e.g. purification products of smoke
    • C04B11/262Calcium sulfate cements strating from chemical gypsum; starting from phosphogypsum or from waste, e.g. purification products of smoke waste gypsum other than phosphogypsum
    • C04B11/264Gypsum from the desulfurisation of flue 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
    • C04B7/00Hydraulic cements
    • C04B7/24Cements from oil shales, residues or waste other than slag
    • C04B7/28Cements from oil shales, residues or waste other than slag from combustion residues, e.g. ashes or slags from waste incineration
    • 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
    • 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
    • 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
    • C04B7/43Heat treatment, e.g. precalcining, burning, melting; Cooling
    • C04B7/438Evacuating at least part of the heat treated material before the final burning or melting step, the evacuated material being used as a cement as such
    • 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

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】 本発明は、気体状硫黄酸化物をカルシウムに結合するこ
とによる、燃焼装置の煙道ガスの脱硫方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for desulfurizing combustion apparatus flue gas by binding gaseous sulfur oxides to calcium.

連邦環境保護法(B工m 5chG )による、及びこ
こで特に空気清浄保持のための技術的基準(TA−Lu
ft)による法規上の規定に基づき、たとえば発電所又
はセメント焼成装置のような工業的燃焼大部装置の運転
は、大気に放出される廃ガスにおいて粒状又は気体状の
汚染物質(たとえば塵、−酸化炭素、二酸化硫黄、窒素
酸化物)の決められた限界値を越えないように行われな
ければなら壜い。
According to the Federal Environmental Protection Act (B-Environmental Protection Act 5chG), and here in particular the Technical Standards for Maintaining Air Cleanliness (TA-Lu
ft), the operation of large industrial combustion units, such as power plants or cement kilns, requires that particulate or gaseous pollutants (e.g. dust, - (carbon oxide, sulfur dioxide, nitrogen oxide) must not be exceeded.

従って特に廃ガスの脱塵及び脱硫のための廃ガス浄化装
置を用いることが必要である。多くの工業的燃焼大盤装
置においては、比較的低濃度の汚染物質を含む極大量の
煙道ガスが発生するので、対応して人減の廃ガス浄化装
置が必要にな夛、これは大匙な研究コスト、続く大きな
投資コスト、運転コスト、保守コスト及び点検コストを
生じさせる。これらコストは、得られる製品で負担され
なけれti’eら寿い。従ってこれらは、経済性及び生
産、競争力ならびに企業家の地位の安全に重荷を負わせ
る。従って、用いられる又は処理のために適する手段を
最適に選び、かつ廃ガス浄化技術及び従って関係する環
境を最大に改善する方策を行うことが必要である。
It is therefore necessary to use waste gas purification devices, especially for the dedusting and desulfurization of waste gases. Many industrial large-scale combustion plants generate extremely large amounts of flue gas containing relatively low concentrations of pollutants, requiring correspondingly reduced-volume waste gas purification equipment, which can be used to This results in significant research costs, followed by large investment costs, operating costs, maintenance costs and inspection costs. These costs must be borne by the resulting product. These therefore place a burden on the economy and production, competitiveness and security of the entrepreneur's position. It is therefore necessary to optimally choose the means used or suitable for the treatment and to take measures that maximize the improvement of waste gas purification technology and therefore of the environment involved.

本発、明は、たとえばボイラー燃焼又はセメント焼成装
置のような工業的燃焼装置の煙道ガス脱硫のための方法
であって、煙道ガスの最適かつ低コストの脱硫を達成で
きる方法を提供するとめう課題に基礎を置く。
The present invention provides a method for the flue gas desulphurization of industrial combustion equipment, such as boiler firing or cement kiln equipment, which provides an optimal and low-cost desulphurization of the flue gas. Based on basic issues.

この課題の解決は、吸収剤として少なくとも部分的に脱
酸素したセメント粗粉を煙道ガスに与えるととKよシ本
発明に従い成功する。
This problem is successfully solved according to the invention if the flue gas is provided with at least partially deoxygenated cement meal as an absorbent.

セメント焼成装置において、少なくとも部分的に脱酸素
したセメント高温粉は中間生成物として極めて好都合に
生じ、これは処理のためにコスト的に嵐い十分量で、気
体状硫黄酸化物のための吸収剤として極めて適している
In cement calciners, an at least partially deoxygenated hot cement powder is very advantageously produced as an intermediate product, which is cost-effective for processing in sufficient quantities and as an absorbent for gaseous sulfur oxides. It is extremely suitable as

これは、硫黄酸化物と酸化カルシウムの硫酸カルシウム
への一転化のために最高の反応活性を有してしる。従っ
て硫黄吸着のために別の吸着剤(たとえば活性炭、純粋
の酸化カルシウム、石灰乳)を外部から供給する又は準
備することは考慮されない。脱硫されるべき廃ガスの導
管に十分に高割合の遊離の酸化カルシウムを含むセメン
ト粗粉を運ぶことだけが必要なことである。
It has the highest reaction activity for the conversion of sulfur oxides and calcium oxide to calcium sulfate. The external supply or preparation of further adsorbents (for example activated carbon, pure calcium oxide, milk of lime) for sulfur adsorption is therefore not considered. It is only necessary to convey cement meal containing a sufficiently high proportion of free calcium oxide into the waste gas line to be desulphurized.

本発明の実施態様として、脱酸素したセメント粗粉を飛
散塵雲の形で煙道ガス流に懸濁し、硫黄酸化物の摂取又
は結合の後に煙道ガス流から分離する。
In an embodiment of the invention, the deoxygenated cement meal is suspended in the flue gas stream in the form of an airborne dust cloud and separated from the flue gas stream after uptake or binding of sulfur oxides.

これによシ、硫黄酸化物と酸化カルシウム含有高温粉の
硫酸カルシウムへの転化が極めて高い転化効率でもって
有利に達成される。
Thereby, the conversion of hot powder containing sulfur oxides and calcium oxide to calcium sulfate is advantageously achieved with extremely high conversion efficiency.

さらに本発明の一実施態様として、セメント粗粉の脱酸
素度は少なくとも50%である。
Furthermore, in one embodiment of the invention, the degree of deoxidation of the cement powder is at least 50%.

この脱酸素度においてすでに、煙道ガスの義硫黄酸化物
に対する粗粉の極めて高i親和性が達成され、それによ
って一層の脱硫が達成されるO 本発明の実施態様において、セメント高温粉は、熱交換
装置の最終段階とロータリーキルン入口室の間のセメン
ト高温粉導管から抜き出される・熱交換管のこの位置で
、予熱された仕込物質の脱酸素は焼成炉の入口前で最大
に進められ、セメント粗粉又はセメント高温粉はここで
最高割合の遊離の酸化カルシウムを有する。
Already at this degree of deoxidation, a very high affinity of the coarse powder for the sulfur oxides of the flue gas is achieved, thereby achieving further desulfurization. In an embodiment of the invention, the cement hot powder is The cement hot powder is withdrawn from the conduit between the final stage of the heat exchanger and the rotary kiln inlet chamber. At this position of the heat exchanger tube, the deoxidation of the preheated feed material is maximized before the inlet of the kiln; Cement coarse powder or cement hot powder here has the highest proportion of free calcium oxide.

また、セメント高温粉導管からセメント高温粉の部分流
を取シ出すことは、公知の装置(たとえば西独特許出願
公開第2815161号参照)により4Iに簡単に行わ
れる。
The removal of a partial stream of hot cement powder from the hot cement powder conduit is also easily carried out using known devices (see, for example, DE 28 15 161 A1).

本発明の別の実施態様では、熱交換装置の最終段階とロ
ータリーキルンの間の主局ガス導管の上部から、部分的
なガス抜出の懸濁物流中のセメント高温粉が抜き出され
る〇 との位置において、予熱ガス流中の熱活性化セメント高
温粉の割合が特に高く、従って比較的少量の懸濁物部分
ガス流が分岐され、これから熱い粗粉が分離され、そし
てこれは硫黄酸化物結合のために煙導ガス導管に加えら
れる。
In another embodiment of the invention, hot cement powder in a partially degassed suspension stream is withdrawn from the upper part of the main station gas line between the final stage of the heat exchanger and the rotary kiln. At this point, the proportion of thermally activated cement hot powder in the preheating gas stream is particularly high, so that a relatively small suspension partial gas stream is branched off, from which hot coarse powder is separated, and this is combined with sulfur oxides. added to the flue gas duct for.

この際、部分ガス流からのセメント高温粉の所定量の取
得が特に有利かつ簡単になる。
In this case, obtaining a predetermined quantity of hot cement powder from the partial gas stream becomes particularly advantageous and simple.

本発明の別の実施態様におい七、ロータリーキルン入口
室の領域から部分的なガス抜出の懸濁物流中のセメント
高温粉が抜き出される。
In another embodiment of the invention, hot cement powder in a partially degassed suspension stream is withdrawn from the region of the rotary kiln inlet chamber.

これにより、アルカリリサイクルの阻止のためのロータ
リーキルン廃ガスの部分抜出のだめの自体公知の又は現
存のバイパス導管との組合せの可能性が生まれる。従っ
てこの際、気化したアルカリに富む焼成炉ガスの一定の
抜出のために役立つ現存の部分ガス抜出導管はまた、煙
道ガスの脱硫のだめの活性なセメント高温粉の取出しの
目的のために用いることができる。
This gives rise to the possibility of combining a sump for the partial withdrawal of rotary kiln waste gases with known or existing bypass lines to prevent alkali recycling. In this case, the existing partial degassing conduits, which serve for the constant withdrawal of the vaporized alkali-rich kiln gases, are also used for the purpose of withdrawal of the hot active cement powder from the flue gas desulphurization sump. Can be used.

本発明のさらに別の実施態様において、抜出されたセメ
ント高温粉は少なくとも部分的に水に溶解される。これ
によ)一方で・セメント高温粉のための担持媒体として
の分岐され鳩い炉廃ガスは望む温度(煙道ガス導管中に
おける温度にiく分対応する)に極めて有利に冷却され
、他方では遊離の酸化カルシウムの一部がやはシ吸着剤
として極めて有利な形態の水酸化カルシウムOa (O
H)2に移行する。
In yet another embodiment of the invention, the extracted hot cement powder is at least partially dissolved in water. As a result, on the one hand, the branched furnace waste gas as carrier medium for the hot cement powder is very advantageously cooled to the desired temperature (corresponding to the temperature in the flue gas line by a fraction i), and on the other hand In this case, some of the free calcium oxide is converted into calcium hydroxide Oa (O
H) Move to 2.

本発明の別の実施態様において、抜き出されたセメント
高温粉は過剰の水と共に煙道ガス流に加こられる。煙道
ガス流中の過剰の水により、廃カスのコンディショニン
グが、フィルター装置(九とえば電気集塵装置)におい
て少しのエネルギー消費で廃ガス流から汚染物質ならび
に反応した吸着剤のほぼ完全な除去が達成されるように
極めて有利に行われる。
In another embodiment of the invention, the extracted hot cement powder is added to the flue gas stream together with excess water. Due to the excess water in the flue gas stream, the conditioning of the waste gas leads to almost complete removal of pollutants as well as reacted adsorbents from the waste gas stream with little energy consumption in filter devices (e.g. electrostatic precipitators). is carried out very advantageously so that it is achieved.

本発明の実施態様において、抜き串されたセメント粗粉
又はセメント高温粉は、熱交換装置に前接される原料の
ための粉砕乾燥装置の直前で煙道ガス流に加えられる。
In an embodiment of the invention, the skewered cement coarse powder or cement hot powder is added to the flue gas stream just before the grinding and drying device for the raw material which is preceded by the heat exchange device.

これにょシ粉砕装置内において、活性セメント高温粉と
二酸化硫黄含有煙道ガス流との強い混合が保証され、硫
黄酸化物と酸化カルシウム0硫酸カルシウムへの転化の
よシ高い効率及びそれによシ煙道ガスのよシ高か脱硫度
が達成される。
This ensures a strong mixing of the activated cement hot powder with the sulfur dioxide-containing flue gas stream in the grinding equipment, resulting in a higher efficiency of the conversion of sulfur oxides and calcium oxides to 0 calcium sulfate, and therefore less smoke. A high degree of desulfurization of the gas is achieved.

本発明の別の一実施態様において、抜き出されたセメン
ト高温粉は、煙道ガス浄化装置の前で煙道ガス流に加え
られる。
In another embodiment of the invention, the extracted hot cement powder is added to the flue gas stream before the flue gas cleaning device.

この際、ある過剰の活性な吸着剤を用い、フィルター内
表面上にたお反応性の吸着剤の薄い活性な層を沈積し、
これにより廃ガスから更に残シのSO2成分を結合する
ことが望ましいと判った。
In this case, an excess of active adsorbent is used to deposit a thin active layer of reactive adsorbent on the inner surface of the filter.
This has shown that it is desirable to further combine residual SO2 components from the waste gas.

反応したセメント高温粉は、フィルターから除去され、
その高1caso4成分含有の故にたとえばセメントミ
ルにおける結合遅延剤としてセメント粉に添加するのに
又は石コウ又は結合剤製造(漆喰)における添加物とし
て適している。
The reacted cement hot powder is removed from the filter and
Due to its high caso4 content it is suitable for addition to cement powders, for example as a bond retarder in cement mills or as an additive in plaster or binder production (stucco).

しかしそれは少なくとも一部、セメント焼成装置の原料
に加えること亀できる。
But it can be added, at least in part, to the raw materials in cement kilns.

本発明により、好ましくはたとえばセメント焼成装置に
地理的に近い・又は隣接する工業的燃焼大型装置たとえ
ば発電所又は他の燃焼装置の煙道ガス脱硫のために吸着
剤としてセメント高温粉を加え、そとで廃ガス脱硫を行
うことの有利な可能性が開かれた。
According to the present invention, cement hot powder is preferably added as an adsorbent for flue gas desulphurization in large industrial combustion units, such as power plants or other combustion units, which are geographically close to or adjacent to cement calcining units. This opens up advantageous possibilities for carrying out waste gas desulphurization.

代理人江崎光好 代理人江崎光史Agent Mitsuyoshi Ezaki Agent Mitsufumi Ezaki

Claims (1)

【特許請求の範囲】 1、 カルシウムに気体状硫黄酸化物を結合することに
よシ燃焼装置の煙道ガスの脱硫を行う方法において、吸
着剤として脱酸素したセメント粗粉を煙道ガスに加える
ことを特徴とすガスに懸濁し、煙道の硫黄酸化物の吸収
又は結合の後に分離する特許請求の範囲第1項記載の方
法。 五 セメント粗粉の脱酸素度が少なくとも50%である
特許請求の範囲第1項又は第2項記載の方法。 4、 セメント粗粉は、セメント製造のための口る特許
請求の範囲第1項〜第3項のいずれか一つに記載の方法
。 5、 脱酸素した高温粉はロータリーキルン−熱交換装
置からの部分ガス抜き出しの懸濁ガス流中で抜舞出され
、分離段階においてガス流から分離される特許請求の範
囲第1項〜第3項のめずれか一つに記載の方法。 6 脱酸素した高温粉はロータリーキルン入口室の領域
からの部分ガス抜き出しの懸濁ガス流中で抜龜出される
特許請求の範囲第1項〜第5項のめずれか一つに記載の
方法。 l 抜き出した高温粉を少なくとも一部、水に溶解する
特許請求の範囲第1項〜6項のいずれか一つに記載の方
法。 & 抜き出した高温粉を過剰の水と共に煙道ガス流に加
える特許請求の範囲第1〜6項のいずれか一つに記載の
方法。 9 抜き出した高温粉を、熱交換装置に前接した原料の
ための粉砕乾燥装置の直前で煙道ガス流に加える特許請
求の範囲第1〜8項のiずれか一つに記載の方法。 10、抜き出した高温粉を煙道ガス浄化装置の前で煙道
ガス流に加える特許請求の範囲第1〜9項のいずれか一
つに記載−の方法。
[Claims] 1. In a method for desulfurizing the flue gas of a combustion apparatus by binding gaseous sulfur oxide to calcium, deoxygenated coarse cement powder is added to the flue gas as an adsorbent. 2. A process according to claim 1, characterized in that the sulfur oxides are suspended in a gas and separated after absorption or binding of the sulfur oxides in the flue. (5) The method according to claim 1 or 2, wherein the degree of deoxidation of the coarse cement powder is at least 50%. 4. The method according to any one of claims 1 to 3, wherein the coarse cement powder is used for manufacturing cement. 5. The deoxygenated hot powder is drawn off in a suspended gas stream of partial degassing from a rotary kiln heat exchanger and separated from the gas stream in a separation stage. The method described in one or more of the following. 6. A method according to claim 1, wherein the deoxygenated hot powder is extracted in a partially degassed suspended gas stream from the region of the rotary kiln inlet chamber. 1. The method according to any one of claims 1 to 6, wherein at least a portion of the extracted high-temperature powder is dissolved in water. & A method according to any one of claims 1 to 6, in which the extracted hot powder is added to the flue gas stream together with excess water. 9. A process according to claim 1, in which the hot powder withdrawn is added to the flue gas stream immediately before the grinding and drying device for the raw material which precedes the heat exchange device. 10. A method according to any one of claims 1 to 9, in which the extracted hot powder is added to the flue gas stream before the flue gas purification device.
JP60000256A 1984-01-07 1985-01-07 Method of desulfurizing flue gas from combustion apparatus Pending JPS60156531A (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
DE3400417.3 1984-01-07
DE3400417 1984-01-07
DE3415210.5 1984-04-21

Publications (1)

Publication Number Publication Date
JPS60156531A true JPS60156531A (en) 1985-08-16

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JP (1) JPS60156531A (en)
DE (1) DE3415210C2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62144736A (en) * 1985-12-18 1987-06-27 メタル ゲゼルシャフト アクチェン ゲゼルシャフト Removal of noxious substance from waste gas
JP2009161415A (en) * 2008-01-10 2009-07-23 Ube Ind Ltd Manufacturing method of cement
CN110683777A (en) * 2019-11-14 2020-01-14 天津水泥工业设计研究院有限公司 Powder desulfurizing agent for cement kiln and preparation method and application thereof

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Publication number Priority date Publication date Assignee Title
DE3536158A1 (en) * 1985-10-10 1986-02-13 Ulf Dipl.-Landw. Dr. 7967 Bad Waldsee Abele Process for the purification from predominantly organic, odour-active compounds of air, exhaust gases and crude gases
US4708855A (en) * 1985-11-07 1987-11-24 Passanaquoddy Tribe Method and system for exhaust gas stream scrubbing
US5100633A (en) * 1985-11-07 1992-03-31 Passamaquoddy Technology Limited Partnership Method for scrubbing pollutants from an exhaust gas stream
DE3643143A1 (en) * 1986-11-05 1988-05-11 Krupp Polysius Ag Process for removing pollutants from exhaust gases
DE19511304A1 (en) * 1995-03-28 1996-10-02 Graf Epe Gmbh Cyclone heat exchanger for heating raw powder as it is fed to cement clinker furnace
DE19936375B4 (en) * 1999-08-03 2008-01-17 Polysius Ag Method for reducing volatile pollutants in the exhaust gases of a heat exchanger system
DE102009020555A1 (en) 2009-05-08 2010-11-11 Ardex Gmbh Method for reducing gaseous sulfur components from the ambient air, caused by emissions from building materials

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT368986B (en) * 1978-04-07 1982-11-25 Lechner Bartl Eiberg Zement METHOD FOR PRODUCING A HYDRAULIC BINDING AGENT
DE3215793A1 (en) * 1982-04-28 1983-11-03 Klöckner-Humboldt-Deutz AG, 5000 Köln METHOD AND DEVICE FOR REDUCING THE SULFURING CIRCUIT AND / OR THE SO (ARROW DOWN) 2 (ARROW DOWN) EMISSION IN A PLANT FOR BURNING FINE GRAIN GOODS

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62144736A (en) * 1985-12-18 1987-06-27 メタル ゲゼルシャフト アクチェン ゲゼルシャフト Removal of noxious substance from waste gas
JP2009161415A (en) * 2008-01-10 2009-07-23 Ube Ind Ltd Manufacturing method of cement
CN110683777A (en) * 2019-11-14 2020-01-14 天津水泥工业设计研究院有限公司 Powder desulfurizing agent for cement kiln and preparation method and application thereof

Also Published As

Publication number Publication date
DE3415210C2 (en) 1995-06-22
DE3415210A1 (en) 1985-07-18

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