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JPS5850926B2 - Production method of calcium nitrite aqueous solution - Google Patents
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JPS5850926B2 - Production method of calcium nitrite aqueous solution - Google Patents

Production method of calcium nitrite aqueous solution

Info

Publication number
JPS5850926B2
JPS5850926B2 JP55045886A JP4588680A JPS5850926B2 JP S5850926 B2 JPS5850926 B2 JP S5850926B2 JP 55045886 A JP55045886 A JP 55045886A JP 4588680 A JP4588680 A JP 4588680A JP S5850926 B2 JPS5850926 B2 JP S5850926B2
Authority
JP
Japan
Prior art keywords
gas
reaction
slaked lime
concentration
calcium nitrite
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.)
Expired
Application number
JP55045886A
Other languages
Japanese (ja)
Other versions
JPS56145106A (en
Inventor
実 遠藤
孝至 草原
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.)
Nissan Chemical Corp
Original Assignee
Nissan Chemical 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 Nissan Chemical Corp filed Critical Nissan Chemical Corp
Priority to JP55045886A priority Critical patent/JPS5850926B2/en
Priority to DK398680A priority patent/DK156168C/en
Priority to CA361,175A priority patent/CA1114133A/en
Priority to SE8006790A priority patent/SE438843B/en
Priority to DE3036605A priority patent/DE3036605C2/en
Priority to NO802873A priority patent/NO154832C/en
Priority to GB8031397A priority patent/GB2074993B/en
Publication of JPS56145106A publication Critical patent/JPS56145106A/en
Publication of JPS5850926B2 publication Critical patent/JPS5850926B2/en
Expired 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
    • C04B22/00Use of inorganic materials as active ingredients for mortars, concrete or artificial stone, e.g. accelerators or shrinkage compensating agents
    • C04B22/08Acids or salts thereof
    • C04B22/085Acids or salts thereof containing nitrogen in the anion, e.g. nitrites
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Ceramic Engineering (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Treating Waste Gases (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Chemically Coating (AREA)
  • Preventing Corrosion Or Incrustation Of Metals (AREA)
  • Pharmaceuticals Containing Other Organic And Inorganic Compounds (AREA)

Description

【発明の詳細な説明】 本発明は、アンモニアを空気酸化することにより得られ
る一酸化窒素及び二酸化窒素含有ガスを消石灰スラリー
に接触吸収させることによる亜硝酸カルシウム水溶液の
製造法の改良に係わる。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improved method for producing an aqueous calcium nitrite solution by contacting and absorbing a gas containing nitrogen monoxide and nitrogen dioxide obtained by air oxidizing ammonia into a slaked lime slurry.

従来より、亜硝酸カルシウムは防錆剤、セメント用混和
剤等として用いられているが、実際に使用する際には、
固体状よりもむしろ30〜40℃程度の水溶液状製品の
提供が望まれている。
Calcium nitrite has traditionally been used as a rust preventive agent, cement admixture, etc., but when actually used,
It is desired to provide a product in the form of an aqueous solution at a temperature of about 30 to 40° C. rather than in a solid state.

亜硝酸カルシウムの水溶液は、固体亜硝酸カルシウムを
水に溶解する方法により容易に得られるが、市販の固体
亜硝酸カルシウムは、亜硝酸カルシウム溶液を濃縮・乾
燥することにより造られたものであるから、この方法は
極めて非効率的である。
An aqueous solution of calcium nitrite can be easily obtained by dissolving solid calcium nitrite in water, but commercially available solid calcium nitrite is made by concentrating and drying a calcium nitrite solution. , this method is extremely inefficient.

高純度及び高濃度の亜硝酸カルシウム水溶液を得る比較
的好ましい方法としては、例えば、特開昭54−431
96号公報に記載の方法が既に知られている。
A relatively preferable method for obtaining a calcium nitrite aqueous solution with high purity and high concentration includes, for example, Japanese Patent Application Laid-Open No. 54-431
The method described in Japanese Patent No. 96 is already known.

この方法は、アンモニアを空気酸化することにより得ら
れるNOとNO2とを含みNo/N02モル比が1.2
〜1.5である高温のガスを、消石灰の20〜40%水
性スラリーに連続的に供給し吸収させ、その際反応温度
を40〜70℃に保ち、未吸収ガスを連続的に排出する
と共に残存消石灰濃度が3〜10係となるまで反応させ
る第1段反応と、次いで第2段反応として、上記未吸収
ガスを回収し酸化させることによって得られるモル比N
O/NO2モル比1.2〜1.5の低濃度にNOとNO
2とを含むガスを、上記第1段反応によって得られる3
〜10φの消石灰を含むスラリーに連続的に供給し、4
0〜700Cで吸収反応させることを主要工程とする方
法である。
This method includes NO obtained by air oxidation of ammonia and NO2, and the No/N02 molar ratio is 1.2.
A high temperature gas of ~1.5% is continuously supplied and absorbed into a 20-40% aqueous slurry of slaked lime, while the reaction temperature is maintained at 40-70°C and unabsorbed gas is continuously discharged. The molar ratio N obtained by recovering and oxidizing the unabsorbed gas in the first stage reaction, which is carried out until the residual slaked lime concentration reaches 3 to 10, and then in the second stage reaction.
NO and NO at low concentrations with an O/NO2 molar ratio of 1.2 to 1.5.
The gas containing 2 is converted into 3 obtained by the above first stage reaction.
Continuously supply slurry containing ~10φ slaked lime,
This is a method whose main step is an absorption reaction at 0 to 700C.

この先行技術は、原料ロスが少なく、かつ、簡易な工程
からなる好ましい方法であるが、大規模の工業生産に適
さない欠点を有する。
Although this prior art is a preferable method with less raw material loss and simple steps, it has the disadvantage that it is not suitable for large-scale industrial production.

すなわち、上記先行技術により、年率数千トンもの工業
生産を行なうには、大型反応器、特に大型冷却器及び大
型空塔酸化器を必要とし、これを改良するために、冷却
速度を高める目的で加圧下70℃以上の高温で反応を行
なわせると、硝酸カルシウムの副生率が増大し、95係
以上の純度を有する亜硝酸カルシウムが得られない。
In other words, according to the above-mentioned prior art, in order to carry out industrial production at an annual rate of several thousand tons, large reactors, especially large condensers and large sky oxidizers are required. If the reaction is carried out under pressure at a high temperature of 70° C. or higher, the by-product rate of calcium nitrate will increase, making it impossible to obtain calcium nitrite having a purity of 95 or higher.

今や、高純度かつ高濃度の亜硝酸カルシウム水溶液の効
率的大規模生産技術の確立が課題である。
The current challenge is to establish efficient large-scale production technology for highly purified and highly concentrated calcium nitrite aqueous solutions.

本発明者らは、詳しい実験的研究を行なった結果、アン
モニア酸化により得られるNOとNO2を含むガスを2
0〜b 収反応させると、以外にも消石灰の溶解度の低下による
反応速度の低下が殆んど起らないことを見出した。
As a result of detailed experimental research, the present inventors found that the gas containing NO and NO2 obtained by ammonia oxidation was
0 to b It has been found that when the reaction is carried out, there is almost no decrease in the reaction rate due to a decrease in the solubility of slaked lime.

更に、NO/NO2のモル比を1.6以上に高めたガス
を消石灰の20〜40係スラリーに加圧下高温で吸収反
応させると、前記硝酸カルシウムの副生率増大が避けら
れるという全く予期し得なかった新事実を見出し、本発
明を完成するに至った。
Furthermore, it was completely unexpected that if a gas with an NO/NO2 molar ratio increased to 1.6 or more was absorbed and reacted with a slurry of 20 to 40 slaked lime at high temperature under pressure, an increase in the by-product rate of calcium nitrate could be avoided. They discovered new facts that had not previously been obtained and completed the present invention.

本発明の第1の目的は、亜硝酸カルシウムの生成割合が
95係以上もの高純度、かつ、30%以上もの高濃度亜
硝酸カルシウム水溶液を得ることにあり、更に他の目的
は、大型設備を要せずに大規模工業生産し得る上記高純
度かつ高濃度亜硝酸カルシウム水溶液の製造方法を提供
することにあり、更に、他の目的は、消石灰スラリー及
びアンモニアの空気酸化により得られる一酸化窒素及び
二酸化窒素含有ガスから簡易な工程により効率よく高純
度かつ高濃度の亜硝酸カルシウム水溶液を製造する方法
を提供することにあり、更に他の目的は、原料消石灰及
び−酸化窒素及び二酸化窒素ガスの損失が少なく効率よ
く高純度かつ高濃度の亜硝酸カルシウム水溶液を製造す
る方法を提供することにある。
The first object of the present invention is to obtain a highly purified calcium nitrite aqueous solution with a calcium nitrite production ratio of 95 or higher and a high concentration of 30% or higher. Another object of the present invention is to provide a method for producing the above-mentioned highly pure and highly concentrated calcium nitrite aqueous solution that can be produced on a large scale without the need for nitrogen monoxide, which is obtained by air oxidation of slaked lime slurry and ammonia. Another object of the present invention is to provide a method for efficiently producing a highly pure and highly concentrated calcium nitrite aqueous solution from raw materials slaked lime and -nitrogen oxide and nitrogen dioxide gas through a simple process. It is an object of the present invention to provide a method for efficiently producing a highly purified and highly concentrated calcium nitrite aqueous solution with little loss.

本発明の製造方法は、0)アンモニアを空気酸化するこ
とにより得られ、一酸化窒素(NO)と二酸化窒素(N
O2)の合計量を5〜12容量係含み、NO/NO2モ
ル比が1.6〜2.5であり、かつ温度が190〜30
0°Cのガスを、消石灰の20〜40重量係水性スラリ
ー中に、その反応温度を75〜1100Cに保ちながら
連続的に供給することにより残存消石灰濃度が2〜10
重量係となるまで吸収反応させ、未吸収ガスは連続的に
反応帯域外・\排出する工程、(ロ)(イ)において排
出された未吸収ガスを回収し、必要に応じ窒素ガスをこ
れに供給し85〜151°Cで酸化することによりNO
/NO2モル比を1.6〜2.5となるように、また、
一酸化窒素と二酸化窒素の合計量が1〜5容量φとなる
ように調節する工程、(ハ)(イ)の工程により得られ
た生成亜硝酸カルシウムが溶解し、残存消石灰濃度2〜
10重量饅の水性スラリー中に、(ロ)の工程により得
られたガスを、そのガスによる2、0〜10kg/−の
圧力下反応温度を75〜1100Gに保ちながら連続的
に供給することにより残存消石灰濃度が3重量φ以下と
なるまで吸収反応させ、未吸収ガスは連続的に反応帯域
外・\排出する工程、に)(ハ)の工程により得られた
液を済過する工程からなることを特徴とする。
The production method of the present invention includes: 0) Ammonia is obtained by air oxidation, and nitrogen monoxide (NO) and nitrogen dioxide (N
The total amount of O2) is 5 to 12 volumes, the NO/NO2 molar ratio is 1.6 to 2.5, and the temperature is 190 to 30
By continuously supplying gas at 0°C into a 20 to 40 weight water-related slurry of slaked lime while maintaining the reaction temperature at 75 to 1100C, the concentration of residual slaked lime can be reduced to 2 to 10%.
The process of absorbing and reacting until it reaches a certain weight, and continuously discharging the unabsorbed gas outside the reaction zone. (B) Collecting the unabsorbed gas discharged in (B), and adding nitrogen gas to it as necessary. NO by supplying and oxidizing at 85-151°C
/NO2 molar ratio from 1.6 to 2.5, and
The step of adjusting the total amount of nitrogen monoxide and nitrogen dioxide to 1 to 5 volumes φ, the produced calcium nitrite obtained in the steps (c) and (b) is dissolved, and the residual slaked lime concentration is 2 to 5.
By continuously supplying the gas obtained in step (b) into a 10 weight cup of aqueous slurry under a pressure of 2,0 to 10 kg/- while maintaining the reaction temperature at 75 to 1100 G. The absorption reaction is carried out until the concentration of residual slaked lime becomes 3 weight φ or less, and the unabsorbed gas is continuously discharged out of the reaction zone, and the liquid obtained in step (c) is passed through. It is characterized by

本発明における亜硝酸カルシウムの生成割合すなわち純
度は、硝酸カルシウム及び亜硝酸カルシウムの生成量に
対する亜硝酸カルシウムの生成量の比で表わされる。
In the present invention, the production rate of calcium nitrite, that is, the purity, is expressed as the ratio of the production amount of calcium nitrite to the production amount of calcium nitrate and calcium nitrite.

本発明に用いられる高濃度消石灰スラリーは、市販工業
用製品の消石灰を水に分散させることにより容易に得ら
れるが、その濃度が20%以下では、上記(イ)〜に)
の工程を結合した方法によっては本発明の目的とする高
濃度の亜硝酸カルシウム水溶液が得られず、また、その
濃度が40%以上では、(イ)の工程において塩基性亜
硝酸カルシウムCa(NO2)・ Ca(OH)22H
20(以下、複塩と称す。
The highly concentrated slaked lime slurry used in the present invention can be easily obtained by dispersing commercially available industrial product slaked lime in water, but if the concentration is 20% or less, the above (a) to)
Depending on the method in which the above steps are combined, the highly concentrated calcium nitrite aqueous solution that is the object of the present invention cannot be obtained, and if the concentration is 40% or more, basic calcium nitrite Ca (NO2 )・Ca(OH)22H
20 (hereinafter referred to as double salt).

)の生成により反応スラリーの粘度が高くなり、−酸化
窒素及び二酸化窒素ガスの吸収を円滑に行なわせ難く、
更に亜硫酸カルシウムの析出をも招来し共に好ましくな
い。
), the viscosity of the reaction slurry increases, making it difficult to absorb nitrogen oxide and nitrogen dioxide gas smoothly;
Furthermore, it also causes precipitation of calcium sulfite, which is both undesirable.

本発明に用いられるアンモニアを空気酸化することによ
り得られるガスは、通常の方法により圧力10に9/−
以下のガスとして容易に得られ、−酸化窒素及び二酸化
窒素5〜12容量係、酸素5〜10容量係、水13〜1
8容量係及び窒素残余優からなる。
The gas obtained by air oxidation of ammonia used in the present invention is prepared by a normal method to a pressure of 10 to 9/-
Easily obtained as the following gases: - Nitrogen oxide and nitrogen dioxide 5 to 12 parts by volume, oxygen 5 to 10 parts by volume, water 13 to 1 part
Consists of 8 capacity factors and nitrogen residuals.

このガスは、先ず、一酸化窒素NOと二酸化窒素NO2
のNO/NO2モル比が1.6〜2.5であることを要
す。
This gas first consists of nitrogen monoxide NO and nitrogen dioxide NO2.
The NO/NO2 molar ratio of 1.6 to 2.5 is required.

このモル比が1.6未満では、ガスを上記(イ)の工程
において消石灰スラリーに吸収反応させる際、硝酸カル
シウムの生成割合が増大し高純度亜硝酸カルシウム水溶
液が得られない。
If this molar ratio is less than 1.6, when the gas is absorbed into the slaked lime slurry in step (a), the proportion of calcium nitrate produced increases, making it impossible to obtain a high-purity calcium nitrite aqueous solution.

また、このモル比が2.5を越えて大きくなる程、(イ
)の工程における一酸化窒素及び二酸化窒素の吸収反応
率が小さくなり反応が非能率的となって好ましくない。
Further, as this molar ratio increases beyond 2.5, the absorption reaction rate of nitrogen monoxide and nitrogen dioxide in the step (a) decreases, and the reaction becomes inefficient, which is not preferable.

しかし、(イ)の工程に用いられるガスとしては、NO
/N02モル比を上記の如く限定するのみでは充分でな
く、更にガス中の一酸化窒素及び二酸化窒素の合計量濃
度を特定範囲に限定することを要す。
However, the gas used in step (a) is NO.
It is not enough to limit the /N02 molar ratio as described above; it is also necessary to limit the total concentration of nitrogen monoxide and nitrogen dioxide in the gas to a specific range.

その濃度が5容量φ以下では反応速度が小さくなり、装
置効率が低下する。
If the concentration is less than 5 volumes φ, the reaction rate will be low and the efficiency of the device will be reduced.

また、−酸化窒素及び二酸化窒素の台形量濃度が高い場
合には、反応上は支障を招来しないが、か\るガスをア
ンモニア酸化法により製造するには、通常12容量饅以
下であることが好ましい。
In addition, if the trapezoidal concentration of -nitrogen oxide and nitrogen dioxide is high, it will not cause any trouble in the reaction, but in order to produce such gas by the ammonia oxidation method, it is usually necessary to have a concentration of 12 volumes or less. preferable.

更にまた、上記アンモニア酸化により得られるガスは、
150°C以下では、ガス中の水蒸気が凝縮し硝酸を生
成す乙ので、本発明の(イ)の工程には150℃以下で
用いることを避けねばならない。
Furthermore, the gas obtained by the above ammonia oxidation is
If the temperature is below 150°C, water vapor in the gas will condense and produce nitric acid, so it is necessary to avoid using the temperature below 150°C in step (a) of the present invention.

このガスの温度が150〜190℃程度では、本発明の
(イ)の工程において、硝酸カルシウムの副生割合が低
下傾向を示すが、反応速度が充分に大とならない。
When the temperature of this gas is about 150 to 190°C, the proportion of calcium nitrate as a by-product tends to decrease in the step (a) of the present invention, but the reaction rate does not become sufficiently high.

このガスの温度が190℃以上となると、本発明の仔)
の工程において硝酸カルシウムの副生割合が著るしく低
下し、反応速度も増大するので本発明の目的が達成され
る。
When the temperature of this gas is 190°C or higher, the present invention
In the process, the by-product ratio of calcium nitrate is significantly reduced and the reaction rate is increased, so that the object of the present invention is achieved.

しかし、このガスの温度が300℃以上にも高くなると
1本発明の(イ)の工程において反応温度を75〜11
0℃に保つために必要な除熱量が著るしく増大するので
効率的でない。
However, if the temperature of this gas rises to 300°C or higher, the reaction temperature in step (a) of the present invention is reduced to 75-11°C.
This is not efficient because the amount of heat removal required to maintain the temperature at 0° C. increases significantly.

反応帯域に供給される前記消石灰スラリー及びガスの量
を増大させて目的物を大量生産するには、除熱速度も高
める必要があり、大型の冷却器によらないでこの課題を
解決するには1反応源度すなわちスラリーの温度を高め
ねばならない。
In order to mass-produce the target product by increasing the amount of the slaked lime slurry and gas supplied to the reaction zone, it is necessary to increase the heat removal rate, and to solve this problem without using a large cooler. 1. The reactant temperature, ie the temperature of the slurry, must be increased.

しかし、前記せ620〜40係の消石灰スラリーは、常
圧下では約70℃においてその水蒸気分圧が前記ガース
中の水蒸気分圧と等しくなるので、反応温度を70℃以
上に保ちながらスラリーの水の蒸発を避けるには、加圧
下に反応を行なわせる必要がある。
However, in the slaked lime slurry of Sections 620 to 40, the partial pressure of water vapor becomes equal to the partial pressure of water vapor in the girth at about 70°C under normal pressure. To avoid evaporation, it is necessary to carry out the reaction under pressure.

前記せる如く、アンモニア酸化により得られるガスは工
業生産上の好ましい圧力としてほぼ10kg/瀝以下の
圧力を有するから高め得るスラリーの最高温度は、ガス
の最大圧力10kg/cnLに対応して約110℃であ
る。
As mentioned above, since the gas obtained by ammonia oxidation has a pressure of approximately 10 kg/f or less as a preferable pressure for industrial production, the maximum temperature of the slurry that can be raised is approximately 110°C corresponding to the maximum gas pressure of 10 kg/cnL. It is.

従って、本発明の(イ)の工程は、スラリーの水蒸発に
基く濃縮を防ぐに充分な圧力下、すなわち供給ガスによ
る2〜10kg/iの圧力下75〜110℃で反応が行
なわれる。
Therefore, in step (a) of the present invention, the reaction is carried out at a temperature of 75 to 110° C. under a pressure sufficient to prevent the slurry from concentrating due to water evaporation, that is, at a pressure of 2 to 10 kg/i by the feed gas.

スラリーの温度が高い捏水酸化カルシウムの溶解度が低
下するにもか\わらず以外にも亜硝酸カルシウムの生成
反応速度が低下しないのは、供給されるガス温が高いこ
とによるものと考えられる。
The reason why the reaction rate for producing calcium nitrite does not decrease even though the solubility of suspended calcium hydroxide decreases when the temperature of the slurry is high is thought to be due to the high temperature of the supplied gas.

本発明の方法によれば、前記ガスを前記スラリー中に反
応温度を上記特定温度に維持しながら連続的に供給し、
未吸収ガスは連続的に反応帯域外へ排出される。
According to the method of the present invention, the gas is continuously supplied into the slurry while maintaining the reaction temperature at the specific temperature,
Unabsorbed gas is continuously vented out of the reaction zone.

上記反応帯域とはガスとスラリーが接触し、反応が生起
する帯域である。
The reaction zone is a zone where gas and slurry come into contact and a reaction occurs.

吸収反応により、ガス中の一酸化窒素及び二酸化窒素は
消費されるが、NO/NO2の消費比率が供給ガス中の
NO/NO2比率とは異なるため、ガスとスラリーとの
接触時間の経過と共にガス中のNO/NO2比率は次第
に高くなり、か\ろガスを長時間スラリーに接触させて
も反応率が著るしく低下し効率的でない。
Due to the absorption reaction, nitrogen monoxide and nitrogen dioxide in the gas are consumed, but since the consumption ratio of NO/NO2 is different from the NO/NO2 ratio in the supplied gas, the gas The NO/NO2 ratio in the slurry gradually increases, and even if the gas is brought into contact with the slurry for a long period of time, the reaction rate decreases significantly and is not efficient.

本発明に従って、NO/NO2モル比が1.6〜2.5
であるガスをスラリーに連続的に供給し、未反応の一酸
化窒素及び二酸化窒素を含む未吸収ガスを反応帯域から
連続的に排出することにより効率的に亜硝酸カルシウム
が生成される。
According to the invention, the NO/NO2 molar ratio is between 1.6 and 2.5.
Calcium nitrite is efficiently produced by continuously supplying a gas to the slurry and continuously discharging unabsorbed gas containing unreacted nitrogen monoxide and nitrogen dioxide from the reaction zone.

更に本発明の方法は、(イ)の工程におけるガスの吸収
反応を残存消石灰濃度が2〜10重量係となったとき停
止する必要がある。
Furthermore, in the method of the present invention, it is necessary to stop the gas absorption reaction in step (a) when the concentration of residual slaked lime reaches 2 to 10% by weight.

10重重量風上にも消石灰を残存させるときは、(ハ)
の工程において多量の低濃度ガスを吸収反応させねばな
らず1反応に長時間を要し好ましくない。
When leaving slaked lime on the windward side, (c)
In the process, a large amount of low concentration gas must be absorbed and reacted, which is undesirable as it takes a long time for one reaction.

また、2重量係以下にまで反応を進めると、上記(イ)
の工程において硝酸カルシウムの生成割合が増大し、高
純度亜硝酸カルシウム水溶液が得られない。
In addition, if the reaction progresses to less than 2 weight ratios, the above (a)
In the process, the production rate of calcium nitrate increases, making it impossible to obtain a high-purity calcium nitrite aqueous solution.

かくして、本発明の(イ)の工程により硝酸カルシウム
の生成及び前記複塩の析出を抑制しながら高能率かつ効
率的に亜硝酸カルシウムを生成させ得るが、この工程で
得られる液から、なお残存する2〜10重の消石灰を分
離除去することは、消石灰の損失を招くのみならず更に
濃縮工程をも必要とし、本発明の目的とする高純度かつ
高濃亜硝酸カルシウム溶液を簡易かつ効率的に製造する
ことができない。
Thus, although calcium nitrite can be produced efficiently and efficiently while suppressing the production of calcium nitrate and the precipitation of the double salt by the step (a) of the present invention, the remaining Separating and removing the 2 to 10 layers of slaked lime not only results in the loss of slaked lime but also requires a further concentration step, making it possible to easily and efficiently produce the high purity and highly concentrated calcium nitrite solution that is the objective of the present invention. cannot be manufactured.

本発明の方法の(ハ)の工程は、(イ)の工程で得られ
る生成亜硝酸カルシウムを溶解せる低濃度消石灰スラリ
ーを更に一酸化窒素及び二酸化窒素を特定モル比にかつ
低濃度に含有するガスに接触させることにより、上記欠
点を解消すると共に、そのガスとして(イ)の工程にお
ける排出ガスをオリ用することにより効率的製造方法を
提供せんとするものである。
In step (c) of the method of the present invention, the low concentration slaked lime slurry that dissolves the produced calcium nitrite obtained in step (a) further contains nitrogen monoxide and nitrogen dioxide at a specific molar ratio and at a low concentration. The purpose is to eliminate the above-mentioned drawbacks by bringing the product into contact with a gas, and to provide an efficient manufacturing method by using the exhaust gas from the step (a) as the gas.

(ハ)の工程に用いられるガスの一酸化窒素及び二酸化
窒素の合計濃度が高いときは、(ハ)の工程において硝
酸カルシウムの生成割合が増大するので好ましくない。
If the total concentration of nitrogen monoxide and nitrogen dioxide in the gas used in step (c) is high, this is not preferable because the proportion of calcium nitrate produced in step (c) will increase.

この(ハ)の工程に用いられるガス中の一酸化窒素及び
二酸化窒素の合計濃度は5容量係以下、特に3容量係以
下が好ましいが、あまり低濃度では亜硝酸カルシウムの
生成速度が小さくなるために通常その濃度は1容量係以
上が適当である。
The total concentration of nitrogen monoxide and nitrogen dioxide in the gas used in this step (c) is preferably 5 volume ratio or less, especially 3 volume ratio or less, but if the concentration is too low, the production rate of calcium nitrite will decrease. Usually, the appropriate concentration is 1 volume or more.

(ハ)の工程に用いられるガスのNO/NO2のモル比
は前記(イ)の工程に用いるガスのモル比についての限
定理由と同じ理由によって1.6〜2.5が好ましい。
The NO/NO2 molar ratio of the gas used in the step (c) is preferably 1.6 to 2.5 for the same reason as the reason for limiting the molar ratio of the gas used in the step (a).

更に、前記(イ)の工程における限定理由と同様の理由
によって、スラリーの水の蒸発を防ぐために供給ガスに
よる2〜10kg/iの圧力下スラリ一温度75〜11
0℃で反応は進められる。
Furthermore, for the same reason as the limiting reason in the step (a) above, in order to prevent water evaporation in the slurry, the slurry at a temperature of 75 to 11% under a pressure of 2 to 10 kg/i by the supply gas.
The reaction proceeds at 0°C.

(ハ)の工程においても、効率よく亜硝酸カルシウムを
生成させるために、ガスは連続的にスラリー中・\供給
され、ガス中の一酸化窒素及び二酸化窒素はスラリーと
の接触によりスラリー中の水酸化カルシウムと反応しそ
の大部分が吸収消費され、而して一酸化窒素及び二酸化
窒素の濃度が低下した未吸収ガスは連続的に反応帯域外
へ排出される。
In the step (c), in order to efficiently generate calcium nitrite, gas is continuously supplied into the slurry, and nitrogen monoxide and nitrogen dioxide in the gas are brought into contact with the slurry to form water in the slurry. The unabsorbed gas that reacts with calcium oxide, most of which is absorbed and consumed, and the concentration of nitrogen monoxide and nitrogen dioxide is reduced, is continuously discharged out of the reaction zone.

(ハ)の工程において、ガスとスラリーとの接触により
亜硝酸カルシウムが更に生成するが、スラリー中の消石
灰を完全に消費させるには長時間ガスの供給を続けねば
ならないから、消石灰を完全に消費させるまでガスを供
給する方法は能率的でない。
In the step (c), calcium nitrite is further produced by the contact between the gas and the slurry, but in order to completely consume the slaked lime in the slurry, the gas must be supplied for a long time, so the slaked lime is completely consumed. It is not efficient to supply gas until the temperature is reached.

(ハ)の工程は、液中に少量のすなわち3係以下、通常
は0.5〜1.5係程度の水酸化カルシウムが残存して
いる状態で反応を停止するのが効率的である。
In the step (c), it is efficient to stop the reaction while a small amount of calcium hydroxide remains in the solution, that is, 3 parts or less, usually about 0.5 to 1.5 parts.

(ハ)の工程に用いられる低濃度に一酸化窒素及び二酸
化窒素を含有するガスとしては、前記(イ)の工程にお
ける排ガスが利用され、これにより一酸化窒素及び二酸
化窒素の損失が避けられる。
As the gas containing nitrogen monoxide and nitrogen dioxide at low concentrations used in the step (c), the exhaust gas from the step (a) is used, thereby avoiding loss of nitrogen monoxide and nitrogen dioxide.

(ロ)の工程は、そのために設けられたものである。The step (b) is provided for this purpose.

前記(イ)の工程における排ガスはNO/NO2モル比
がほぼ4以上であるので、これを回収し、モル比を1.
6〜2.5に調節する必要がある。
Since the exhaust gas in the step (a) has a NO/NO2 molar ratio of approximately 4 or more, it is collected and the molar ratio is reduced to 1.
It is necessary to adjust it to between 6 and 2.5.

このモル比の調節には空塔酸化器を用い、これに(イ)
の工程における排ガスを導通することにより、排ガス中
に含まれる4〜5容量φの酸素によって一酸化窒素を酸
化することにより容易に行なうことができる。
A sky tower oxidizer is used to adjust this molar ratio, and (a)
This can be easily carried out by conducting the exhaust gas in the process of 2 to oxidize nitrogen monoxide with 4 to 5 volumes of oxygen contained in the exhaust gas.

この酸化反応は、排ガスを空塔酸化器中に85〜150
℃で充分な時間滞留させることにより容易に進行させ得
る。
In this oxidation reaction, the exhaust gas is fed into an air column oxidizer with a temperature of 85 to 150
This process can be easily carried out by staying at ℃ for a sufficient period of time.

好都合なことに、(イ)の工程における排出ガスは、通
常90〜1300Cの温度にあるから。
Advantageously, the exhaust gas in step (a) is usually at a temperature of 90 to 1300C.

特別の加熱を要せずに酸化器中を通過させることにより
容易に酸化させることができる。
It can be easily oxidized by passing it through an oxidizer without requiring special heating.

更に好都合なことに、(イ)の工程の排ガスは、尚高い
圧力を有するから、空塔酸化器は大型のものを要せずに
上記酸化反応を行なわせ得る。
Furthermore, advantageously, since the exhaust gas in step (a) still has a high pressure, the above-mentioned oxidation reaction can be carried out without requiring a large-sized sky tower oxidizer.

場合によっては、空塔酸化器の代りにパイプを用いるこ
ともでき、本発明によれば、前記冷却器の小型化と共に
、上記酸化器も小型化することができ、工業生産上の利
益は多大である。
In some cases, a pipe may be used instead of the sky tower oxidizer, and according to the present invention, the oxidizer can be downsized as well as the cooler, which brings great benefits in industrial production. It is.

−酸化窒素及び二酸化窒素の合計濃度を1〜5容量係と
なるように調節することは、必要に応じ窒素ガスを排ガ
スと共に空塔酸化器へ供給することにより容易に行ない
得る。
- The total concentration of nitrogen oxide and nitrogen dioxide can be easily adjusted to 1 to 5 volumes by supplying nitrogen gas to the sky oxidizer together with the exhaust gas, if necessary.

しかし、(イ)の工程に用いられるガスとして一酸化窒
素及び二酸化窒素の合計濃度が5〜12容量係であるア
ンモニアを空気酸化することにより得られるガスを用い
るときは、(イ)の工程における排ガス中の一酸化窒素
及び二酸化窒素の合計濃度が5咎以下、通常1〜3容量
多となり、特に濃度調節を要せずに充分に(ハ)の工程
に用いられる。
However, when using a gas obtained by air oxidation of ammonia in which the total concentration of nitrogen monoxide and nitrogen dioxide is 5 to 12 volumes as the gas used in the step (a), The total concentration of nitrogen monoxide and nitrogen dioxide in the exhaust gas is 5 volumes or less, usually 1 to 3 volumes higher, and can be used in the step (c) without any particular concentration adjustment.

本発明の方法によれば、上記(イ)、(ロ)、及び(ハ
)の工程を結合することにより高濃度に亜硝酸カルシウ
ムを含む水溶液が得られるが、(ハ)の工程で得られる
溶液中には少量の消石灰の他、原料中に含まれていた不
溶性不純物が存在することもあり、それを分離除去する
ことにより高純度かつ高濃度の亜硝酸カルシウム水溶液
が得られる。
According to the method of the present invention, an aqueous solution containing calcium nitrite at a high concentration can be obtained by combining the above steps (a), (b), and (c); In addition to a small amount of slaked lime, insoluble impurities contained in the raw materials may also be present in the solution, and by separating and removing them, a highly pure and highly concentrated calcium nitrite aqueous solution can be obtained.

上記(ハ)の工程により得られる溶液は容易に濾過する
ことができるので、不純物の分離除去の工程としてに)
の濾過工程を付加設定するのが好ましい。
The solution obtained in step (c) above can be easily filtered, so it can be used as a step to separate and remove impurities)
It is preferable to additionally set up a filtration step.

濾過は通常の方法により行ない得る。Filtration can be carried out by conventional methods.

本発明の方法は、回分式、連続式のいずれの方式でも実
施することができる。
The method of the present invention can be carried out either batchwise or continuously.

好ましい実施態様は、連続式プロセスである。A preferred embodiment is a continuous process.

すなわち、第1反応槽に、スラリー中の消石灰濃度を2
〜10重量係に保ちながら高濃度消石灰スラリーと、高
濃度に一酸化窒素及び二酸化窒素を含有するガスを連続
的に供給し、消石灰スラリーとガスを接触させ、同時に
第1反応槽からはその内容液を連続的にとり出し、これ
を第2反応槽へ移送し、一方、第1反応槽における未吸
収ガスは第1反応槽から連続的に排出し、これを回収し
空塔酸化器・\連続的に供給し、酸化することによりモ
ル比調節した後、得られたガスを第2反応槽へ連続的に
供給し、第1反応槽から送られた液と接触させ、未吸収
ガスを連続的に排出すると共に、液を連続的にとり出し
、これを濾過器・\供給し、濾過することにより連続的
に高純度かつ高濃度の亜硝酸カルシウム水溶液が得られ
る。
That is, the concentration of slaked lime in the slurry was set to 2 in the first reaction tank.
A highly concentrated slaked lime slurry and a gas containing nitrogen monoxide and nitrogen dioxide at a high concentration are continuously supplied while maintaining the weight of the slaked lime slurry at ~10% by weight, and the slaked lime slurry and the gas are brought into contact with each other. The liquid is continuously taken out and transferred to the second reaction tank, while the unabsorbed gas in the first reaction tank is continuously discharged from the first reaction tank and recovered. After adjusting the molar ratio by supplying and oxidizing the obtained gas, the obtained gas is continuously supplied to the second reaction tank and brought into contact with the liquid sent from the first reaction tank, and the unabsorbed gas is continuously removed. At the same time, a highly pure and highly concentrated calcium nitrite aqueous solution is continuously obtained by continuously taking out the liquid, supplying it to a filter, and filtering it.

また、別の実施態様としては、0うの工程ヲ経た後、(
ハ)の工程における排ガスを再回収し、(ロ)の工程と
同様にして再度、モル比及び必要ならば濃度も調節する
工程(dX−付加設定し、(ハ)の工程で得られた液を
連続的に回収し、これに上記(口′)の工程で得られる
ガスを連続的に供給して接触吸収させ、未吸収ガスを連
続的に排出する工程(バ)を付加設定し、(バ)の工程
で得られる液を連続的にとり出し、これを濾過する方法
も採用し得る。
Moreover, as another embodiment, after passing through the 0 steps, (
The process of recovering the exhaust gas from step (c) again and adjusting the molar ratio and, if necessary, the concentration again in the same manner as step (b) (dX-addition setting, and the liquid obtained in step (c)) A step (b) is additionally set in which the gas obtained in the above step (') is continuously collected, the gas obtained in the above step (') is continuously supplied, the gas is catalyzed and absorbed, and the unabsorbed gas is continuously discharged. A method may also be adopted in which the liquid obtained in step (b) is continuously taken out and filtered.

上記同様にして、更に(口“)、(四″)・・・及び(
ハ“)、(ハ“′)・・・の多段階の工程を付設し残存
水酸化カルシウムの濃度が3重量係以下好ましくは1係
以下となるまで反応させる方法も実施することができる
In the same manner as above, further (mouth "), (four")... and (
It is also possible to carry out a method in which the multi-stage steps of c"), (c"'), etc. are added and the reaction is carried out until the concentration of residual calcium hydroxide becomes 3 parts by weight or less, preferably 1 part or less.

しかし、設備面において効率よ〈実施するには、簡易な
(イ)、(ロ)、(ハ)及びに)の工程を結合した方法
が最も好ましい。
However, in terms of equipment, it is most preferable to combine the simple steps (a), (b), (c), and (c) for efficiency and implementation.

本発明の方法によれは、設備として大型のものを要せず
に、効率よく30〜400〜40重量%の、かつ、亜硝
酸カルシウムの生成割合95係以上の高純度亜硝酸カル
シウム水溶液が製品として工業的に大量生産でき、この
ものは直接に防錆剤、セメント混和剤等 して用いられ
る。
According to the method of the present invention, a high-purity calcium nitrite aqueous solution of 30 to 400 to 40% by weight and a calcium nitrite production ratio of 95% or higher can be efficiently produced as a product without requiring large-sized equipment. It can be industrially mass-produced as a rust preventive agent, cement admixture, etc.

以下実施例を挙げて更に詳しく説明するが、本発明の技
術的範囲はこれに限定されるものではない。
The present invention will be described in more detail below with reference to Examples, but the technical scope of the present invention is not limited thereto.

実施例 1 直径2.0m高さ3.8mの第1反応槽中に工業用1級
消石灰1750kg、亜硝酸カルシウム85kg及び水
4500kgを入れて撹拌しスラリーとした後、撹拌し
ながら槽底部に設けられた多孔ノズルよりアンモニアの
空気酸化によって製造した一酸化窒素及び二酸化窒素の
濃度9.4容量係、一酸化窒素と二酸化窒素のモル比(
NO/NO2)1.7、温度約230°Cのガスを13
00 Nm/h rの速度で、80時間連続的に吹き込
み未吸収ガスは連続的に排出した。
Example 1 1,750 kg of industrial grade 1 slaked lime, 85 kg of calcium nitrite, and 4,500 kg of water were put into a first reaction tank with a diameter of 2.0 m and a height of 3.8 m, stirred to form a slurry, and then placed at the bottom of the tank while stirring. The concentration of nitrogen monoxide and nitrogen dioxide produced by air oxidation of ammonia through a porous nozzle was 9.4 by volume, and the molar ratio of nitrogen monoxide and nitrogen dioxide (
NO/NO2) 1.7, gas at a temperature of about 230°C 13
The gas was continuously blown at a rate of 0.00 Nm/hr for 80 hours, and the unabsorbed gas was continuously discharged.

この間、反応糸の圧力は2.8kg1cr&に、また、
反応液は冷却して78ないし83°Cに保ち、pH値を
11以上に保持した。
During this time, the pressure of the reaction thread was 2.8kg1cr&,
The reaction solution was cooled and maintained at 78-83°C, and the pH value was maintained above 11.

かくして亜硝酸カルシウム30.4%、硝酸カルシウム
1.1%、水酸化カルシウム3.4係を含む反応液8.
5トンを得た。
Thus, the reaction solution containing 30.4% calcium nitrite, 1.1% calcium nitrate, and 3.4% calcium hydroxide.8.
Obtained 5 tons.

この間の排出ガス中の未吸収−酸化窒素及び二酸化窒素
の合計量の濃度は、はぼ2.0容量係であった。
During this period, the concentration of the total amount of unabsorbed nitrogen oxide and nitrogen dioxide in the exhaust gas was about 2.0 volume.

次に、上記液を第2反応槽に移し、第1反応槽から排出
するガス全量を空塔酸化器・\通し、一酸化窒素と二酸
化窒素のモル比(NO/No□ )をほぼ1.7に調整
したのち、槽底部に設けられた多孔ノズルより連続的に
吹き込み1反応系圧力を2.5kg/CI?Lに、液温
を75ないし80℃に、pHを11以上に保ちながら8
.0時間反応させると共に未吸収ガスを連続的に排出し
た。
Next, the above liquid is transferred to a second reaction tank, and the entire amount of gas discharged from the first reaction tank is passed through an air column oxidizer, so that the molar ratio of nitrogen monoxide to nitrogen dioxide (NO/No□) is approximately 1. After adjusting to 7, the pressure of one reaction system was 2.5 kg/CI? by continuously blowing from the porous nozzle provided at the bottom of the tank. 8 while keeping the liquid temperature at 75 to 80°C and the pH at 11 or higher.
.. The reaction was continued for 0 hours, and unabsorbed gas was continuously discharged.

かくして亜硝酸カルシウム34.O重量幅、硝酸カルシ
ウム1.4重量%、水酸化カルシウム12重量%、その
他固型分1.4重量係を含む液8.6トンを得た。
Thus calcium nitrite34. 8.6 tons of liquid containing 1.4% by weight of calcium nitrate, 12% by weight of calcium hydroxide, and 1.4% by weight of other solids was obtained.

この間排出ガス中の一酸化窒素及び二酸化窒素の合計量
濃度はほぼ0.4容量係であった。
During this period, the total concentration of nitrogen monoxide and nitrogen dioxide in the exhaust gas was approximately 0.4 volume.

ここに得られた液を冷却後濾過して亜硝酸カルシウム3
31重量%、硝酸カルシウム1,5重量%の清澄な亜硝
酸カルシウム水溶液を得た。
The obtained liquid was cooled and filtered to obtain calcium nitrite 3.
A clear calcium nitrite aqueous solution containing 31% by weight and 1.5% by weight of calcium nitrate was obtained.

実施例 2 亜硝酸カルシウム濃度29.5重量%、硝酸カルシウム
1.1重量%、水酸化カルシウム含有率4重量%の水性
スラリーを8.5トン内容せる第1反応槽へ、消石灰含
有率29.8重量%の水性スラリーを約750kg/H
の速度で、またNO/NO2モル比1.7、−酸化窒素
及び二酸化窒素の合計量濃度9.4容量気温度約230
℃のアンモニア酸化により得られたガスを130ONm
”/)] の速度で撹拌下槽底から第1反応槽へそれ
ぞれ連続的に供給した。
Example 2 8.5 tons of an aqueous slurry having a calcium nitrite concentration of 29.5% by weight, a calcium nitrate content of 1.1% by weight, and a calcium hydroxide content of 4% by weight was fed into a first reaction tank with a slaked lime content of 29.5% by weight. Approximately 750 kg/H of 8% by weight aqueous slurry
Also, the NO/NO2 molar ratio is 1.7, - the total amount of nitrogen oxide and nitrogen dioxide concentration is 9.4, and the volume temperature is about 230
The gas obtained by ammonia oxidation at 130 ONm
"/)] were continuously supplied from the bottom of the tank to the first reaction tank under stirring.

反応系圧力を2.8kg/fflに、反応温度を78〜
83℃に保ち、第4反応槽から連続的に約1000 k
g/Hの速度で内容物を排出し、また、未反応消石灰濃
度は4重量%に保った。
The reaction system pressure was set to 2.8 kg/ffl, and the reaction temperature was set to 78~
Maintained at 83℃ and continuously heated for approximately 1000 k from the 4th reaction tank.
The contents were discharged at a rate of g/h, and the concentration of unreacted slaked lime was maintained at 4% by weight.

第1反応槽からは、未吸収ガスが連続的に排出され、−
酸化窒素及び二酸化窒素の合計濃度は1,9容量係であ
った。
Unabsorbed gas is continuously discharged from the first reaction tank, and -
The total concentration of nitrogen oxide and nitrogen dioxide was 1.9 volumes.

このガスは全量そのま\空塔酸化器・\導通され、NO
/NO2モル比1.7に調節された。
The entire amount of this gas is passed through the sky tower oxidizer as it is, and the NO
/NO2 molar ratio was adjusted to 1.7.

第1反応槽から連続的に排出された液はそのまま第2反
応槽・\連続的に供給され、上記調節ガスは連続的に第
2反応槽へ供給された。
The liquid continuously discharged from the first reaction tank was continuously supplied as it was to the second reaction tank, and the regulating gas was continuously supplied to the second reaction tank.

第2反応槽では、撹拌子液温75〜80℃に、圧力2.
5kg/−に、また、液中水酸化カルシウム濃度は約1
.5重量優に保たれ1反応液は1000kg/Hの速度
で連続的に排出された。
In the second reaction tank, the stirrer liquid temperature was 75 to 80°C and the pressure was 2.
5 kg/-, and the concentration of calcium hydroxide in the liquid is about 1
.. One reaction solution was kept at a weight of 5.5 and was continuously discharged at a rate of 1000 kg/H.

この液は冷却後連続的に濾過器・\供給され、沢過され
た。
After cooling, this liquid was continuously supplied to a filter and thoroughly filtered.

炉液は亜硝酸カルシウムを32.4重量饅と硝酸カルシ
ウムを1.6重量饅含み透明な水溶液であった。
The furnace solution was a clear aqueous solution containing 32.4 weight of calcium nitrite and 1.6 weight of calcium nitrate.

Claims (1)

【特許請求の範囲】 1 (イ)アンモニアを空気酸化することにより得られ
、一酸化窒素(NO)と二酸化窒素(NO2)を5〜1
2容量多含み、No/N02モル比が1.6〜2.5で
ありかつ温度が190〜300’Cのガスを、消石灰の
20〜40重量係水性スラリー中に前記ガスによる2、
0〜10kg/−の圧力平反温度を75〜110℃に保
ちながら連続的に供給することにより残存消石灰濃度が
2〜10重量係重量性まで吸収反応させ、末吸収ガスは
連続的に反応帯域外・\排出する工程、(ロ)(イ)に
おいて排出された末吸収ガスを回収し、必要に応じ窒素
ガスをこれに供給し、85〜1508Cで酸化させるこ
とによりNo/N02モル比を1.6〜2.5となるよ
うに、また、一酸化窒素と二酸化窒素の合計量が1〜5
容量φとなるように処理する工程、 (ハ)(イ)の工程により得られた生成亜硝酸カルシウ
ムが溶解し、残存消石灰濃度が2〜10重量係重量性ス
ラリー中に、(ロ)の工程により得られたガスを、その
ガスによる2、0〜10kg/CrILの圧力下反応温
度を75〜110℃に保ちながら連続的に供給すること
により残存消石灰濃度が3重量係以下となるまで吸収反
応させ、未吸収ガスは連続的に反応帯域外・\排出する
工程、に)(ハ)の工程により得られた液を濾過する工
程からなることを特徴とする高純度かつ高濃度亜硝酸カ
ルシウム水溶液の製造法。
[Claims] 1 (a) Obtained by air oxidation of ammonia, containing nitric oxide (NO) and nitrogen dioxide (NO2) of 5 to 1
A gas containing a large volume of 20 to 40% by weight, a No/N02 molar ratio of 1.6 to 2.5, and a temperature of 190 to 300'C is added to a water-related slurry of 20 to 40% by weight of slaked lime.
By continuously supplying the pressure of 0 to 10 kg/- while keeping the temperature at 75 to 110°C, the residual slaked lime concentration is absorbed and reacted to a weight ratio of 2 to 10%, and the final absorbed gas is continuously removed from the reaction zone.・\Discharging process (b) Collect the end absorption gas discharged in (a), supply nitrogen gas to it as necessary, and oxidize it at 85 to 1508C to bring the No/N02 molar ratio to 1. 6 to 2.5, and the total amount of nitrogen monoxide and nitrogen dioxide is 1 to 5.
Step (c) Processing the produced calcium nitrite obtained in step (a) to dissolve the residual slaked lime concentration in the slurry having a weight ratio of 2 to 10, step (b). By continuously supplying the gas obtained by the gas under a pressure of 2.0 to 10 kg/CrIL while maintaining the reaction temperature at 75 to 110°C, an absorption reaction is carried out until the concentration of residual slaked lime becomes 3 weight coefficient or less. A highly pure and highly concentrated calcium nitrite aqueous solution comprising the following steps: (2) filtering the liquid obtained in step (c), and continuously discharging unabsorbed gas outside the reaction zone. manufacturing method.
JP55045886A 1980-04-08 1980-04-08 Production method of calcium nitrite aqueous solution Expired JPS5850926B2 (en)

Priority Applications (7)

Application Number Priority Date Filing Date Title
JP55045886A JPS5850926B2 (en) 1980-04-08 1980-04-08 Production method of calcium nitrite aqueous solution
DK398680A DK156168C (en) 1980-04-08 1980-09-19 PROCEDURE FOR PREPARING Aqueous SOLUTION OF CALCIUM NITRIT
CA361,175A CA1114133A (en) 1980-04-08 1980-09-29 Process for producing aqueous solution of calcium nitrite
SE8006790A SE438843B (en) 1980-04-08 1980-09-29 PROCEDURE FOR PREPARING A WATER SOLUTION OF CALCIUM NITRIT WITH HIGH PURITY AND HIGH CONCENTRATION
DE3036605A DE3036605C2 (en) 1980-04-08 1980-09-29 Process for preparing an aqueous solution of calcium nitrite
NO802873A NO154832C (en) 1980-04-08 1980-09-29 PROCEDURE FOR THE PREPARATION OF AN Aqueous SOLUTION OF CALCIUM NITRIT.
GB8031397A GB2074993B (en) 1980-04-08 1980-09-29 Process for producing aqueous solution of calcium nitrite

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP55045886A JPS5850926B2 (en) 1980-04-08 1980-04-08 Production method of calcium nitrite aqueous solution

Publications (2)

Publication Number Publication Date
JPS56145106A JPS56145106A (en) 1981-11-11
JPS5850926B2 true JPS5850926B2 (en) 1983-11-14

Family

ID=12731716

Family Applications (1)

Application Number Title Priority Date Filing Date
JP55045886A Expired JPS5850926B2 (en) 1980-04-08 1980-04-08 Production method of calcium nitrite aqueous solution

Country Status (7)

Country Link
JP (1) JPS5850926B2 (en)
CA (1) CA1114133A (en)
DE (1) DE3036605C2 (en)
DK (1) DK156168C (en)
GB (1) GB2074993B (en)
NO (1) NO154832C (en)
SE (1) SE438843B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60105116U (en) * 1983-12-21 1985-07-18 株式会社吉野工業所 Primary molded product of biaxially stretched blow molded bottle

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2011163587A1 (en) * 2010-06-25 2011-12-29 Board Of Governors For Higher Education,State Of Rhode Island And Providence Plantations Self-mending composites incorporating encapsulated mending agents
EP3536677A1 (en) * 2018-03-05 2019-09-11 Yara International ASA A setting and hardening accelerator for a cement, mortar or concrete composition, optionally comprising supplementary cementitious materials, and use of this accelerator

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA967723A (en) * 1970-04-01 1975-05-20 Martin M. Wendel Manufacture of nitrites
JPS5443196A (en) * 1977-09-13 1979-04-05 Nissan Chem Ind Ltd Prduction of aqueous solution of calcium nitrite

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60105116U (en) * 1983-12-21 1985-07-18 株式会社吉野工業所 Primary molded product of biaxially stretched blow molded bottle

Also Published As

Publication number Publication date
CA1114133A (en) 1981-12-15
DK398680A (en) 1981-10-09
GB2074993B (en) 1983-08-10
JPS56145106A (en) 1981-11-11
NO802873L (en) 1981-10-09
GB2074993A (en) 1981-11-11
NO154832B (en) 1986-09-22
DK156168C (en) 1989-12-04
SE8006790L (en) 1981-10-09
DK156168B (en) 1989-07-03
SE438843B (en) 1985-05-13
DE3036605C2 (en) 1987-04-16
DE3036605A1 (en) 1981-10-15
NO154832C (en) 1987-01-07

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