JPS58104022A - Manufacture of crystallite synthetic anhydride - Google Patents

Manufacture of crystallite synthetic anhydride

Info

Publication number
JPS58104022A
JPS58104022A JP20219782A JP20219782A JPS58104022A JP S58104022 A JPS58104022 A JP S58104022A JP 20219782 A JP20219782 A JP 20219782A JP 20219782 A JP20219782 A JP 20219782A JP S58104022 A JPS58104022 A JP S58104022A
Authority
JP
Japan
Prior art keywords
calcium
anhydride
heat treatment
flue gas
synthetic
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
JP20219782A
Other languages
Japanese (ja)
Inventor
ウルリヒ・モ−ン
ヴオルフガング・ブロス
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.)
Hitachi Zosen Inova Steinmueller GmbH
Original Assignee
L&C Steinmueller GmbH
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 L&C Steinmueller GmbH filed Critical L&C Steinmueller GmbH
Publication of JPS58104022A publication Critical patent/JPS58104022A/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
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • 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
    • 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

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Ceramic Engineering (AREA)
  • Analytical Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • General Chemical & Material Sciences (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Treating Waste Gases (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (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】 ルシウム2水塩を含む排煙脱硫中間生成やからなる微結
晶混合物から微結晶の形の合成無水物を製造する方法に
関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a process for producing synthetic anhydrides in the form of microcrystals from a microcrystalline mixture consisting of flue gas desulfurization intermediates containing lucium dihydrate.

無水物は各1の方法で製造できる。製造法に応じて、天
然無水物と合成無水物とに分類される◎天然無水物は下
記の方法によって製造できる。
Anhydrides can be produced by one method. Depending on the production method, they are classified into natural anhydrides and synthetic anhydrides.◎Natural anhydrides can be produced by the following method.

a)天然産無水物の採掘および処理 b)天然の硫酸カルシウム2水塩(石膏)の加熱脱水 上記方法にもとづいて一表した無水物は反応が緩慢であ
るため、そのままの状態では、建材工業に使用できす、
建材工業に使用するために更に処理しなければなら々い
。この場合、、微粉砕以外に、複数の添加物( ?I,
lえに反応促進剤)を加える会費がある,。
a) Mining and processing of naturally produced anhydrous materials b) Heating dehydration of natural calcium sulfate dihydrate (gypsum) The anhydrous materials listed above based on the above method react slowly, so if they are used as they are, they cannot be used in the building materials industry. It can be used for
It must be further processed for use in the building materials industry. In this case, in addition to fine grinding, multiple additives (?I,
There is a fee to add reaction accelerator).

合成無水物は、鳩知のごとく、フッ化水素酸の製造の際
Km生する。この無水物も、微粉砕し、反応性を改善す
る添加物管脚えなければ建材工業において使用できない
。合成無水物は、更に、乾式焼成操作によって化学石膏
から調製できる。更K、排煙脱硫物から合成無水物を得
ることもできる。この場合、亜硫酸カルシウム含有成分
および吸収剤残渣を公知の方法で湿式酸化して硫酸カル
シウム2水塩に転化し、次いで、この2水塩を脱水処1
11..て無水物とする〇 建拐工業において使用される天然無水物および合成無水
物は、更に、セメント工業において、D I N 42
08 K規定される無水物結合材として、または、汎用
建材(例えば、むねの夷持材、控参の結合材成分として
使用でき、る。
Km of synthetic anhydrides are produced during the production of hydrofluoric acid, as in Hatochi. This anhydride cannot be used in the building materials industry unless it is finely ground and added with additives to improve the reactivity. Synthetic anhydrides can also be prepared from chemical gypsum by a dry calcination operation. Furthermore, synthetic anhydrides can also be obtained from flue gas desulfurization products. In this case, the calcium sulfite-containing component and the absorbent residue are wet-oxidized to calcium sulfate dihydrate in a known manner, and this dihydrate is then subjected to a dehydration treatment.
11. .. The natural anhydrides and synthetic anhydrides used in the Jiankui industry are further processed into D I N 42 in the cement industry.
It can be used as an anhydride binder specified in the 08K standard, or as a binder component for general-purpose building materials (e.g., bracing materials for breasts, and binders for supporting materials).

−知の通シ、各種のプロ七゛トス(例えば、排煙脱硫プ
ロセス)において、゛亜−(−カルシウム半水塩および
硫酸カルシウム2水塩を含み、合成無水物の製造原料と
なり得る中間生成物が生ずる。
- Commonly known, in various processes (e.g. flue gas desulfurization process), an intermediate product containing calcium hemihydrate and calcium sulfate dihydrate, which can be used as a raw material for the production of synthetic anhydrides. Something comes into being.

従って、本発明の目的は、亜硫酸カルシウム半水塩およ
び硫酸カルシウム2水塩を含む排煙脱硫生成物を使用し
、適切な処理を行なって、反応性添加物を使用すること
なしに建材工llK使用できる物理的な形状の合成無水
物を調製できる方法を提供することにある。
It is therefore an object of the present invention to use flue gas desulfurization products containing calcium sulfite hemihydrate and calcium sulfate dihydrate and, with appropriate treatment, to manufacture building materials without the use of reactive additives. The object is to provide a method by which synthetic anhydrides can be prepared in a usable physical form.

この目的を達成するため、本発明によれば1ljkの存
在下で、200〜900’Cの温度範囲において熱処理
を行うことKよシ、排煙脱硫中間生成物中の亜硫酸カル
シウム生木塩含有成分を、まず、脱水して亜硫酸カルシ
ウムを生成させ、次いでこれを酸化して硫酸カルシウム
を生成させ、一方、上記中間生成物中の硫酸カルシウム
2水塩含有成分を脱水する方法を提供される。
To achieve this objective, according to the invention, a heat treatment is carried out in the temperature range of 200 to 900'C in the presence of 1 ljk, and the calcium sulfite raw wood salt-containing component in the flue gas desulfurization intermediate product is is first dehydrated to produce calcium sulfite, which is then oxidized to produce calcium sulfate, while dehydrating the calcium sulfate dihydrate-containing component in the intermediate product.

湿式排煙脱硫法の中間生成物を使用する場合は、本発明
の好ましい夾施態様にもとづき、熱部amに、混合物を
少くとも部分的に機械的およびまた・′:j9 は熱的に処理して脱水せしめる。
If an intermediate product of the wet flue gas desulphurization process is used, according to a preferred embodiment of the invention, the mixture is at least partially mechanically and/or thermally treated in the hot zone am. and dehydrate.

本発明の方法によって得られる利点は、排煙脱硫生成物
は、熱処理中および熱部11MK伴う反応時に有するよ
うな微結晶構造をすでに有していると云う点rcある。
The advantage obtained by the method of the invention is that the flue gas desulfurization product already has a microcrystalline structure, as it has during the heat treatment and during the reaction involving the hot section 11MK.

従って、かくして得られた無水物はそのまま使用でき1
%殊の用途においてのみ添加物を加えれによい0 爽に、本発明で得られる無水物は、公知の無水物と同様
、充填@(例えば、砂)と混合できる。
Therefore, the anhydride thus obtained can be used as is.
Additives may only be added in special applications.Additionally, the anhydride obtained according to the invention can be mixed with fillers (eg, sand) like known anhydrides.

更に、本発明で得られる無水物は、公知の方法で焼hV
I−だ半水石膏と混合し、て、多相石膏を製造できる。
Furthermore, the anhydride obtained in the present invention can be annealed by a known method.
It can be mixed with I-hemihydrate gypsum to produce multiphase gypsum.

本発明の無水物は大きな用途として、セメントの凝結―
部側として使用できる。この場合、本発明の無水物は、
単独でも使用できるが、半水石膏゛と混合して使用する
こともできる。この場合、半水石膏は天然物でも合成物
でもよい。
The anhydride of the present invention has a major use in cement setting.
Can be used as a side. In this case, the anhydride of the present invention is
It can be used alone, but it can also be used in combination with gypsum hemihydrate. In this case, the gypsum hemihydrate may be natural or synthetic.

更に、セメント工業において”最終混合物1に使用でき
るように、合成無水物と乾燥した排煙石膏とを混合すれ
ば有利である。
Furthermore, it is advantageous to mix the synthetic anhydride with the dried flue gas gypsum so that it can be used in the cement industry in the final mixture 1.

未処理の最終生成物である“排煙石膏“と比較(て、価
値の高い建築用材料が得られ、その市場価格が高いので
、排煙脱硫法の経済性が改善される。
Compared to the untreated final product "flue gas gypsum", a high value building material is obtained and its market price is high, improving the economics of the flue gas desulfurization process.

排煙脱硫生成物から無水物を1!!造する公知の方法で
は、低い…値において水性懸濁液中の亜硫酸カルシウム
半水塩を、空気を添加し7て硫酸カルシウム2水塩に酸
化している。脱硫生成物は、概ね、未反応の徴収剤を含
んでいるので、酸化に4b*な低いpH餉を得るKFi
相轟な量の硫酸を添加しなければならない。酸化処HA
K続いて、機械的、熱的脱水処理を行う。
1 anhydride from flue gas desulfurization products! ! In a known method for producing calcium sulfite hemihydrate in an aqueous suspension at low values, it is oxidized to calcium sulfite dihydrate by the addition of air. Since the desulfurization product generally contains unreacted collectors, it is possible to obtain a low pH level that is less susceptible to oxidation.
A large amount of sulfuric acid must be added. Oxidation treatment HA
Then, mechanical and thermal dehydration treatment is performed.

上記の方法に比較して、本発明の方法では、硫酸を添加
する必要はなく、また亜硫酸カルシウムを硫酸カルシウ
ム半水塩化する際に発生する酸化熱を熱的脱水に利用で
きると云う利点がある。
Compared to the above methods, the method of the present invention has the advantage that it is not necessary to add sulfuric acid and that the oxidation heat generated when calcium sulfite is converted into calcium sulfate hemihydrate can be used for thermal dehydration. .

本発明の合成無水物の製造方法を、以下の実施例を参照
して更に説明する。
The method for producing the synthetic anhydride of the present invention will be further explained with reference to the following examples.

実施例1 諏1図は本発明の方法を集施するための装亀系を示す。Example 1 Figure 1 shows a system for implementing the method of the present invention.

ボイラーの排ガースはメイラ−を出た稜、必要あれば脱
塵し、ついで硫黄酸化物の分離のための洗#装−″に送
る。この場合、排ガスは洗浄機内で石kk含壱懸濁液と
振触させる。この洗浄用i!濁液は循環して使用する。
The exhaust gas from the boiler exits the mailer, is dedusted if necessary, and is then sent to a washing machine to separate sulfur oxides.In this case, the exhaust gas is suspended in the washing machine, including stones. Shake with the solution.This i! suspension for cleaning is used by circulation.

反応生&*、は部分流として取出t7.4!!械的に脱
水処理する。本実施例ではこのため、湿式ヤイクロンお
よびドラムフィルターを使用した。亜硫酸カルシウム半
水塩を硫酸カルシウム2水塙Kll化するためK、洗浄
後の溜りに空気を吹込むことかできる。洗浄機の榴り内
で酸化を行つことは、次の工程での機械的脱水に有利で
ある。他方、かくして、熱処理KIIIして放出きれる
鹸化熱力:少くなるので、洗浄塔での際化度が高くなる
とh4済的最適性が失われる。
The reaction product &* is taken out as a partial stream t7.4! ! Dehydrate mechanically. For this reason, a wet YACRON and drum filter were used in this example. In order to convert calcium sulfite hemihydrate into two liters of calcium sulfate, air can be blown into the pool after washing. Performing the oxidation in the washer shell is advantageous for mechanical dewatering in the next step. On the other hand, the thermal power of saponification that can be released after heat treatment KIII is reduced, so that if the degree of saponification in the washing tower becomes high, the optimization of the saponification process is lost.

機械的に脱水した生rJL物は熱処理装置に送って更に
脱水し、なお存在する亜硫酸カルシウムを酸化する。こ
の場合、所要熱量は全体的にまたは部分的yc g比熱
から得られる。−足的に必豐表エネルギーは、全体的K
または111!、b″□□!的に、高m#ガスの供給に
よりまたは発電所の燃焼空気からおよび(またFi)燃
料の燃焼によって得ることができる。
The mechanically dehydrated raw rJL product is sent to a heat treatment unit for further dehydration and to oxidize any calcium sulfite still present. In this case, the heat requirement is obtained wholly or partially from the yc g specific heat. -The required surface energy is the overall K
Or 111! , b″□□! can be obtained by supplying high m# gas or from the combustion air of the power plant and by combustion of (also Fi) fuel.

#1図に示す実施例では固形物含量約7〜10重量−の
懸濁液を洗浄機内を循環させる。$11!械的脱水は残
存水分がIQ−15重量−になるまで行う。洗浄機中に
空気を吹込むことによシ亜硫酸カルシv) A半水塩の
95−以上が硫酸カルシウム2水塩に酸化される。最終
的に、最高温間が5150Cの2段階熱処理によって合
成無水物を調珈する。亜硫酸カルシウムは残存しない。
In the embodiment shown in Figure #1, a suspension having a solids content of about 7-10% by weight is circulated through the washer. $11! Mechanical dehydration is carried out until the residual moisture reaches IQ-15 weight. By blowing air into the washer, more than 95 of the calci sulfite v) A hemihydrate is oxidized to calcium sulfate dihydrate. Finally, the synthetic anhydride is prepared by a two-step heat treatment at a maximum temperature of 5150C. No calcium sulfite remains.

かくして得られる無水物の幾つかの性質を以下に示す。Some properties of the anhydride thus obtained are shown below.

D I N 42011 K規定される試験を行った結
果を以下に示す。
The results of the tests specified in DIN 42011K are shown below.

推奨用途: DIN 4208 K規定される無水物結
合材、セメント添加剤 D I N 420Bに規定される試験を行った結果を
以下に示す。
Recommended uses: Anhydride binder specified by DIN 4208K, cement additive Test results specified by DIN 420B are shown below.

推奨用適:凝結が速いので、抗這用噴射材として使用で
きる・ 実施例2 第2図は本発明の方法を実施するための別の有利な装置
を示す。排ガスの処理は、実施例1と同様である。
Recommended use: Due to its rapid setting, it can be used as anti-crawling propellant. Example 2 FIG. 2 shows another advantageous apparatus for carrying out the method of the invention. The treatment of exhaust gas is the same as in Example 1.

洗浄用懸濁液の循環路から取出した部分流は、部分的に
機械的に予備脱水J1LIIする。このためK例えば、
湿式サイクロンまたは真空フィルターを使用できる。洗
浄塔における酸化は単に排ガス中に@1れる酸素によっ
て行われる。機械的に予備脱水した懸濁液/スラッジは
、乾燥装置において加熱乾燥する。この場合、できる限
り費費の不要な排熱(1111えば、脱1ife置に送
る前の排ガス)管使柑すべきである。予備乾嚢tた混合
物は次いで別の熱処理装置に送シ残存水の駆除および亜
硫酸カルシウムの硫酸カルシウムへの酸化を行つ。この
場合、@2熱処理工程の所要熱量の大部分は、夷−例1
とは異なシ、酸化熱から得られる。安価なまたは無料の
排熱によって予備乾燥を行うことができれば、このI!
施例の方tは、エネルギー的に実施ipHlの方法よυ
も有利である。
The partial stream taken off from the washing suspension circuit is partially mechanically pre-dehydrated J1LII. For this reason, K, for example,
Wet cyclones or vacuum filters can be used. The oxidation in the scrubbing tower is carried out solely by the oxygen present in the exhaust gas. The mechanically pre-dehydrated suspension/sludge is heated and dried in a drying device. In this case, waste heat (e.g., exhaust gas before being sent to a decommissioning unit) should be used as much as possible without any expense. The pre-desiccant mixture is then sent to another heat treatment device to remove residual water and oxidize calcium sulfite to calcium sulfate. In this case, most of the heat required for @2 heat treatment step is
It is obtained from the heat of oxidation. If pre-drying can be done with cheap or free waste heat, this I!
In the example, the method of energetically implementing ipHl is υ
is also advantageous.

実施例3 第3図は本発明を奥施する丸めの他の装置系を示す。?
イラーの排ガスは必l!に応じて予備脱塵装置を通過さ
せて、最終生成物に対する要件を満足できるよう脱塵す
る。
Embodiment 3 FIG. 3 shows another rounding device system embodying the present invention. ?
Ira's exhaust gas is a must! Depending on the requirements, the product may be passed through a pre-dedusting device to be dedusted to meet the requirements for the final product.

次いで排ガスを、懸濁液の形の吸収剤を排ガス中に噴霧
する噴S吸収装置に送る。この場合、上記懸濁液は、排
ガスの熱によって乾燥される。上記噴霧と並行して、硫
黄酸化物の分離が行われる。
The exhaust gas is then sent to a spray S absorption device which sprays absorbent in the form of a suspension into the exhaust gas. In this case, the suspension is dried by the heat of the exhaust gas. In parallel with the above spraying, separation of sulfur oxides takes place.

噴霧吸収装置に続いて設置されているダスト分離器にお
いて反応生成物が本質的な排塵および未反応の粉塵とと
もに分離される。上記混合物の一部は吸収剤の利用度を
改譬するため噴霧吸収装置にもどすことができる。残部
を、本発明に係る熱処理装置に送って処理する・ 排煙脱硫装置から来る中間生成物は熱処理の九め、ロー
タリー中ルン内で、例えば、45’Cて約1時間加熱す
る一中間生成物は上記処11によって、・:′ 乾燥され、微粉化される。熱処理前後の組成管下表:熱
部l!#Jの中間生成物および熱処理後の無水物(S分
分析値) 上記の無水物試料をセメント製造実験に使用し。
The reaction products are separated from the essential waste dust and unreacted dust in a dust separator installed next to the spray absorption device. A portion of the mixture can be returned to the spray absorber to modify absorbent utilization. The remainder is sent to the heat treatment device according to the present invention for treatment. The intermediate product coming from the flue gas desulfurization device is heated in a rotary chamber for about 1 hour at, for example, 45'C in the ninth step of the heat treatment. The material is dried and pulverized in step 11 above. Composition of tube before and after heat treatment Table below: Heat section l! Intermediate product of #J and anhydride after heat treatment (S content analysis value) The above anhydride sample was used in a cement production experiment.

た口 この場合、実験用が一ルミル中でセメントタリン、/7
2.713 fおよび無水物287tをプレイン(Bl
ains ’)  比表面積が4.0OOos”/fと
なるように粉砕17た。
In this case, cement talin, /7
2.713 f and 287 t of anhydride in plain (Bl
ains') was ground 17 so that the specific surface area was 4.0OOos''/f.

この場合セメントクリンカに添加した無水物の蓋は、D
INl164シート1第2.2.4項に規定されるSO
1添加@ 3.5重量%に対応する。
In this case, the anhydride cap added to the cement clinker is D
SO as specified in Section 2.2.4 of INl 164 Sheet 1
1 addition @ 3.5% by weight.

かくして得られたIルトランドセメントの性質を下表に
示した。
The properties of the I Rutland cement thus obtained are shown in the table below.

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

第1図〜第3図は本発明の方法に使用する装置系を示す
。 手続補正書(方式) 昭和57年12月16日 特許庁長官殿 1、事件の表示 昭和57年 特許願 第20219’i’号2、発明の
名称 微結晶合成無水物の製造方法 3、補正をする者 事件との関係   特許出願人 住所痺シ冑)−に/;告’′”t!y5y>−° 1−
名 称   チル・ラン暫・ツエ・シュタインミュラア
書ゲゼル/ヤフト・、ット・ベシュレンクテル・ノ飄フ
ツング4、代理人 〒105住所 東京都港区西新橋1丁目1番15号物産
ビル別館 電話(591) 02616、補正の内容 別紙の通ム 図面の浄書内容に変更なし
1 to 3 show the apparatus system used in the method of the invention. Procedural amendment (method) December 16, 1980 Mr. Commissioner of the Japan Patent Office 1, Indication of the case 1982 Patent application No. 20219'i' 2, Title of invention Process for producing microcrystalline synthetic anhydride 3, Amendment Relationship with the patent applicant's address
Name: Chill Lan Shimbun Tsue Steinmüller Gesell/Yaft Beschlenkter Note Futsung 4, Agent Address: 105 Address: Bussan Building Annex, 1-15 Nishi-Shinbashi, Minato-ku, Tokyo Telephone: 591) 02616, Contents of amendment No changes to the engraving contents of the attached drawing.

Claims (1)

【特許請求の範囲】 1、亜硫酸カルシウム半水塩と硫酸カルシウム2水場と
を含む排煙脱硫中間生成物の微結晶混合−から微結晶の
形の合成無水物を製造する方法において、@索の存在下
、200〜900°Cの温度で熱処理を行うことにより
、前記中間生成物中の!m#にカルシウム半水塩含有成
分を脱水して、ま1、亜硫酸カルシウムを生成させ次い
で、酸化1−で’trAttllkカルシウムを生成さ
せ、一方、中間生成物中σ〕竜除カルシウム2水塩含有
成分を脱水することを特徴とする、微結晶合成無水物の
#!造方法。 2・ 湿式排煙脱硫混合物を使用する場合には、熱処理
前に、混合物を機械的およびまたは熱的に、少くとも部
分的に脱水する触杆請求の範囲第1璃記私の方法。 8・ 熱処理に会費な熱エネルギーは、外部からの給熱
により、および(lたFi)亜硫酸カルシウムの硫酸カ
ルシウムへの転化反応にwAL=て発生する酸化熱によ
って供給する特許請求の範囲第;項または第2項記載の
方法。
[Scope of Claims] 1. A method for producing a synthetic anhydride in the form of microcrystals from a microcrystalline mixture of flue gas desulfurization intermediate products containing calcium sulfite hemihydrate and calcium sulfate 2 water bodies. ! in the intermediate product by carrying out a heat treatment at a temperature of 200-900°C in the presence of ! m# is dehydrated with calcium hemihydrate-containing component to produce (1) calcium sulfite, and then oxidized (1-) to produce 'trAttllk calcium, while in the intermediate product σ] containing calcium dihydrate # of microcrystalline synthetic anhydride, which is characterized by dehydrating the ingredients! Construction method. 2. If a wet flue gas desulphurization mixture is used, the mixture is at least partially dehydrated mechanically and/or thermally before the heat treatment. 8. Thermal energy necessary for the heat treatment is supplied by external heat supply and by oxidation heat generated in the conversion reaction of (ltaFi)calcium sulfite to calcium sulfate. Or the method described in Section 2.
JP20219782A 1981-11-21 1982-11-19 Manufacture of crystallite synthetic anhydride Pending JPS58104022A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE331461433 1981-11-21
DE19813146143 DE3146143C2 (en) 1981-11-21 1981-11-21 Process for the production of synthetic anhydrite in finely crystalline form

Publications (1)

Publication Number Publication Date
JPS58104022A true JPS58104022A (en) 1983-06-21

Family

ID=6146863

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20219782A Pending JPS58104022A (en) 1981-11-21 1982-11-19 Manufacture of crystallite synthetic anhydride

Country Status (6)

Country Link
JP (1) JPS58104022A (en)
BE (1) BE895068A (en)
DE (1) DE3146143C2 (en)
DK (1) DK497882A (en)
FR (1) FR2516908B1 (en)
NL (1) NL8204425A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109876759A (en) * 2019-04-09 2019-06-14 昆山宇顺环保科技有限公司 Accelerate the method and device of Desulphurization sulfite calcium oxidation using low temperature waste gas

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SE438846B (en) * 1982-11-12 1985-05-13 Flaekt Ab PROCEDURE AND DEVICE FOR CLEANING OF GAS GAS FROM SULFUR DIOXIDE
DE3539261A1 (en) * 1985-11-06 1987-05-07 Hoelter Heinz Anhydrite for the production of dam construction materials in mining
AT391465B (en) * 1986-08-26 1990-10-10 Donau Chemie Ag Method of processing chloride-rich flue gas desulphurization material (FGD material) to produce cement clinker
DE3719284A1 (en) * 1986-10-08 1988-04-21 Krc Umwelttechnik Gmbh METHOD FOR THE DISPOSAL OF WET FLUE GAS DESULFURATION PLANTS
DE3827612A1 (en) * 1988-08-13 1990-02-15 Viktor Dr Ing Gobiet Building material for use in underground operation
DE19708907C1 (en) * 1997-03-05 1998-04-16 Gfr Aufbereitung Reststoffe Processing organic material-contaminated gypsum waste
US8962730B2 (en) * 2012-11-27 2015-02-24 The Goodyear Tire & Rubber Company Self-healing rubber composition and tire

Family Cites Families (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB454239A (en) * 1935-03-25 1936-09-25 Francis Robert Himsworth Process for the production of anhydrous calcium sulphate and plasters made therefrom
DE2406054A1 (en) * 1974-02-08 1975-08-21 Fels Werke Peine Salzgitter METHOD OF CATALYTIC OXYDATION OF CALCIUM SULFITE
GB1547423A (en) * 1975-03-31 1979-06-20 Japan Government Gypsum whisker composites
GB1504688A (en) * 1975-04-11 1978-03-22 Exxon Research Engineering Co Mitigating or preventing environmental pollution by sulphur oxides in the treatment of sulphur-containing substance
DE2708984C2 (en) * 1977-03-02 1984-12-06 Hölter, Heinz, Dipl.-Ing., 4390 Gladbeck Process for the production of calcium sulfate hemihydrate
DE2833382B2 (en) * 1978-07-29 1980-10-23 Saarbergwerke Ag, 6600 Saarbruecken Process for the utilization of the gypsum produced in flue gas desulphurization systems that are operated on a lime basis
DE2833757C2 (en) * 1978-08-01 1986-10-16 Richard E. Norristown Pa. Valiga Process for hardening inorganic, aqueous waste sludge
US4595576A (en) * 1981-09-04 1986-06-17 A/S Niro Atomizer Process for flue gas desulfurization
DE3135200A1 (en) * 1981-09-05 1983-03-17 L. & C. Steinmüller GmbH, 5270 Gummersbach METHOD FOR TREATING END PRODUCTS FROM THE FLUE GAS DESULFURATION

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109876759A (en) * 2019-04-09 2019-06-14 昆山宇顺环保科技有限公司 Accelerate the method and device of Desulphurization sulfite calcium oxidation using low temperature waste gas

Also Published As

Publication number Publication date
FR2516908A1 (en) 1983-05-27
DE3146143C2 (en) 1986-06-19
DK497882A (en) 1983-05-22
DE3146143A1 (en) 1983-06-01
FR2516908B1 (en) 1986-06-27
BE895068A (en) 1983-03-16
NL8204425A (en) 1983-06-16

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