WO2005068356A1 - Method for producing hydrogen fluoride - Google Patents
Method for producing hydrogen fluoride Download PDFInfo
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- WO2005068356A1 WO2005068356A1 PCT/JP2005/000552 JP2005000552W WO2005068356A1 WO 2005068356 A1 WO2005068356 A1 WO 2005068356A1 JP 2005000552 W JP2005000552 W JP 2005000552W WO 2005068356 A1 WO2005068356 A1 WO 2005068356A1
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- fluorine
- calcium
- fluoride
- sulfuric acid
- hydrogen fluoride
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B7/00—Halogens; Halogen acids
- C01B7/19—Fluorine; Hydrogen fluoride
- C01B7/191—Hydrogen fluoride
- C01B7/192—Preparation from fluorspar
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/12—Halogens or halogen-containing compounds
- C02F2101/14—Fluorine or fluorine-containing compounds
Definitions
- the present invention relates to a method for producing hydrogen fluoride, and more particularly, to a method capable of effectively utilizing fluorine in a fluorine-containing solution to reduce the amount of solid waste.
- the present invention relates to a method for producing hydrogen nitride.
- the treatment of a fluorine-containing solution such as a fluorine-containing wastewater is performed by reacting with a calcium compound such as quick lime, slaked lime or calcium chloride to fix most of the fluorine as hardly soluble calcium fluoride.
- a calcium compound such as quick lime, slaked lime or calcium chloride.
- further treatments such as the aluminium / minium salt method, the fluoroapatite method, the activated alumina method, the basic anion exchange resin method, and the A1 chelate resin method are carried out.
- the calcium fluoride obtained by the immobilization treatment in this way has a very fine particle size and cannot be filtered as it is, so it is flocculated using a flocculant, and then subjected to sedimentation separation and filter press filtration. I have.
- the water content is as high as 50 to 80%, making it difficult to reuse it for industrial purposes. Therefore, a part of the generated calcium fluoride sludge is returned to its original state, and the amount of sludge to be discarded is reduced by increasing the particle size at least a little by giving a role of seed crystal (for example, Drainage, Vol. 42, No. 10, page 27-32 (2000)).
- An object of the present invention is to fix fluorine present in a solution such as wastewater as calcium fluoride, use it as a raw material for hydrogen fluoride production, and use calcium fluoride produced as a by-product of hydrogen fluoride production as a solution. It is used to fix fluorine in water.
- the company will produce hydrogen fluoride, a key material in the fluorine chemical industry, without using, and provide a fluorine recycling system that uses sulfuric acid as a by-product to fix fluorine in wastewater.
- the gist of the present invention is that calcium sulfate produced as a by-product in the production of hydrogen fluoride is used for immobilizing fluorine in a fluorine-containing solution, and calcium fluoride obtained by the immobilization is reacted with sulfuric acid.
- a method for producing hydrogen fluoride comprising producing hydrogen fluoride, and subjecting the by-produced calcium sulfate to the step of immobilizing fluorine in the fluorine-containing solution.
- Figure 1 is a conceptual diagram of the fluorine recycling system of the present invention.
- FIG. 2 shows a hydrogen fluoride generator used in an example (beaker test) of the present invention.
- FIG. 3 shows a hydrogen fluoride generator used in an embodiment (pilot test) of the present invention.
- the method for producing hydrogen fluoride of the present invention calcium sulfate by-produced in producing hydrogen fluoride is used for immobilizing fluorine in a fluorine-containing solution, and the fluoride obtained by the immobilization is used. Hydrogen fluoride is produced by reacting calcium with sulfuric acid. To a step of immobilizing fluorine in a fluorine-containing solution.
- the fluorine-containing solution is not particularly limited, and fluorine-containing wastewater discharged from various production processes can be suitably used.
- the calcium sulfate used for immobilizing fluorine may be anhydrous, hemihydrate or gypsum.
- Fluorine immobilization reaction (C a SO 4 + 2 F- ⁇ C a F 2 + SO 4 2 one: Equation (2)) is solid one-pack reaction salt exchange, yet retaining the shape of the calcium sulfate Since the reaction proceeds as it is, the average particle size of calcium sulfate is preferably 200 ⁇ m or less. In consideration of increasing the purity of the calcium fluoride after the reaction and filterability, 10 to 200 / zm is preferable, and 30 to 150 ⁇ is more preferable. However, exceeding 200 ⁇ only decreases the content of fluorinated calcium, and does not hinder use in the next hydrogen fluoride production process.
- the calcium fluoride obtained in the present invention has excellent sedimentation properties, and can be easily dehydrated by ordinary filtration means. For example, when dehydration is performed using a normal suction filtration device in a laboratory, calcium fluoride having a water content of about 25 to 35% can be obtained. Furthermore, the use of a centrifugal dehydrator or a filter press can easily reduce the water content to about 15 to 20%. Compared to 50-60%, it can be less than half. In producing hydrogen fluoride by reacting the resulting fluoridated solution with sulfuric acid, it is preferable to use calcium fluoride having a water content of 40% or less, and more preferably to a water content of 25%. It is as follows.
- the calcium fluoride obtained in the present invention has a loss on ignition (500 ° C, 1 hour) after drying (120 ° C, 2 hours) of 5% or less, preferably 3% or less, usually It is around 2%, which is different from that obtained by ordinary fluorine immobilization treatment at 7 to 10%.
- the calcium fluoride obtained in the present invention can be dried with a small amount of energy due to a small amount of water and a small loss on ignition, and is suitable as a raw material for producing hydrogen fluoride.
- the bulk specific gravity is about 1/2 to 1/3 smaller than that of fluorite. This is because fluorite is almost crystalline but porous.
- Fluorite used as a raw material for the production of hydrogen fluoride is generally a powder having an average particle size of about 50 to 100 ⁇ m and containing about 10% water to prevent scattering. The whole amount is imported from overseas.
- the reaction between fluorite and sulfuric acid with good crystallinity gradually progresses from the surface of the fluorite, and is covered with the generated sulfuric acid. Therefore, the mixture is sufficiently mixed and then mixed with a rotary kiln. It is usually carried out at a temperature of up to 500 ° C. for 6 to 8 hours. However, the large particles do not react completely, leaving calcium fluoride in the core.
- the calcium fluoride obtained in the present invention is a porous and polycrystalline substance, and the reaction of the above formula (3) occurs smoothly. Therefore, the reaction is usually completed in about 200 ° C. for about 1 hour. It is possible even below 150 ° C. As described above, the relatively mild reaction conditions cause the equipment materials and reactor The range of choices will be expanded, and it will be possible to design inexpensive and compact equipment.
- the reaction when the calcium fluoride obtained by the immobilization is reacted with sulfuric acid to produce hydrogen fluoride, the reaction is usually carried out at a temperature of 250 ° C. or lower, preferably 100 ° C. or less. It can be performed at 200 ° C. It is preferable that the content of calcium fluoride used is higher, but there is no problem even if the content is about 60%, as described later, since most of the impurities are calcium sulfate.
- the calcium fluoride obtained by the reaction of the formula (2) hardly contains silica, which is a major impurity of fluorite, and therefore has the advantage of not producing the problematic by-product ky hydrofluoric acid. Have.
- the sulfuric acid to be used is fuming sulfuric acid or a mixture of fuming sulfuric acid and sulfuric acid.
- the amount of sulfuric acid is proportional to the content of calcium fluoride, but it is preferable to use sulfuric acid having an equivalent amount or less with respect to the amount of calcium fluoride. is there. An excessive amount of sulfuric acid remains in the generated calcium sulfate and is not preferable because it is wasted. On the other hand, if the amount is less than the equivalent, unreacted calcium fluoride remains, but it is used for the next immobilization of fluorine. In order to increase the recovery rate of hydrogen fluoride and the corrosion resistance of the apparatus, it is preferable to minimize the amount of water present in the reaction system.
- fuming sulfuric acid that matches the amount of water in the sulfuric acid and the water loss corresponding to the ignition loss of calcium fluoride, or prepare a fuming sulfuric acid of about 10% by mixing fuming sulfuric acid and sulfuric acid in advance. It is preferable to keep it. As described above, in the present invention, it is most preferable to use sulfuric acid in an amount equivalent to 0.8 times the amount of calcium fluoride.
- the solid content mainly composed of calcium sulfate by-produced in this reaction is preferably pulverized to an average particle diameter of 200 ⁇ m or less in order to use the solid content of fluorine in a fluorine-containing solution.
- the pulverization may be either dry or wet.
- slaked lime, hydroxylated It is preferable to adjust the pH of the fluorine-containing solution to 5 to 9 by adding an alkaline substance such as sodium.
- the calcium sulfate in the method of mixing calcium sulfate with a fluorine-containing solution and fixing and recovering fluorine in the solution as calcium fluoride, has a particle diameter of 10 to 200.
- ⁇ is Paiiota, and the molar ratio of calcium in the calcium sulfate to fluorine (M ca / 2 M F) (wherein, M ca / the number of moles of calcium; M F is the number of moles of fluorine).
- force SO 8 or more Less than 1.2.
- the molar ratio is preferably at least 0.8 and less than 1.1.
- fluorine can be recovered from various fluorine-containing solutions by immobilizing it as calcium fluoride having a relatively large particle size and good filterability. This method is particularly useful when the obtained calcium fluoride is not used for the production of hydrogen fluoride but is recovered using a membrane such as a hollow fiber membrane or a filter press.
- Anhydrous gypsum produced as a by-product in a hydrofluoric acid production brand was pulverized (average particle size: 65 ⁇ ) (100 g) and inorganic fluoride synthetic wastewater (fluorine concentration: 8,800 ppm) (40 kg). , Placed in a 50 L polyethylene reaction vessel equipped with a stirrer, stirred for 1 hour, and settled solids for a while Then, the supernatant was removed, and the mixture was dehydrated using a suction filter to collect 820 g of a solid.
- the collected solids are ground to 200 ⁇ m or less, of which 353.2 g and inorganic fluoride synthetic wastewater (fluorine concentration of 12,200 ppm)
- the solid matter recovered in the same manner as in Example 2 was similarly immobilized with fluorine without being ground.
- the calcium fluoride content in the obtained solid was 56%.
- Example 2 252.3 g of the solid obtained in Example 1 (lost loss of 1.7%, calcium fluoride content of 87.8%, calcium sulfate content of 10.5%) was prepared from a fluororesin PFA.
- 5% fuming sulfuric acid prepared by mixing sulfuric acid and 25% fuming sulfuric acid
- 27.8.3 g of sulfuric acid made of fluoroplastic PFA It was weighed on a dropping funnel and set as shown in Fig.2. Slowly add 5% fuming sulfuric acid, and after confirming that sulfuric acid has become sufficiently compatible with calcium fluoride, gradually raise the temperature of the oil path and raise the temperature to 180 ° C over 3 hours. I let it.
- Example 6 7,003 g of solid matter obtained by treating calcium sulfate and inorganic fluorine compound synthetic wastewater (loss on ignition 1.8%, calcium fluoride content 91.2%, calcium sulfate content 7.0%) Put into a Hastelloy C22 10 L reaction vessel (11) equipped with a stirrer, steam jacket, thermometer, etc., and add 5% fuming sulfuric acid equivalent to the theoretical amount of calcium fluoride put in the reaction vessel (11%). (Prepared by mixing sulfuric acid and 25% fuming sulfuric acid) 8,034 g was weighed into a sulfuric acid dropping funnel (12) made of fluororesin PFA, and set as shown in Fig. 3 (A is Calcium fluoride, B is sulfuric acid).
- the collected solid is ground to 200 ⁇ or less, and the entire amount is made up of inorganic fluoride synthetic wastewater (fluorine concentration: 12,100 ppm). And stirred. To make the pH of the slurry solution neutral, 670 g of a 20% aqueous calcium hydroxide solution was added. One hour later, the stirring was stopped to allow a solid to settle for a while, and then the supernatant was removed, followed by dehydration using a suction filter to recover 8,498 g of the solid.
- Example 6 The solid obtained in Example 6 (ignition loss 2.3 ° /., Calcium fluoride) (91.5%, calcium sulfate content 7.2%) 6, 998 g was placed in a 10 L reaction vessel made of Hastelloy C22 equipped with a stirrer, steam jacket, thermometer, etc., and reacted. 5% fuming sulfuric acid (prepared by mixing sulfuric acid and 25% fuming sulfuric acid) corresponding to the theoretical amount of calcium fluoride in a container 8,045 g was weighed into a sulfuric acid dropping funnel made of fluoroplastic PFA. And set as shown in Figure 3. After slowly dropping 5% fuming sulfuric acid with stirring, steam was flowed through the jacket to gradually raise the temperature. The internal temperature was raised to 150 ° C.
- the collected solid is ground to 200 ⁇ or less, and the entire amount is made up of inorganic fluoride synthetic wastewater (fluorine concentration: 12,100 ppm). And stirred. To make the pH of the slurry liquid neutral, 712 g of a 20% aqueous calcium hydroxide solution was added. After 1 hour, stirring was stopped to allow a solid to settle for a while, then the supernatant was removed, and dehydration was performed using a suction filter to recover 8,416 g of the solid.
- hydrogen fluoride which is a key material of the fluorine chemical industry, is capable of efficiently immobilizing fluorine in a solution and not using natural calcium fluoride (fluorite) which is scarce in resources.
- fluorine recycling system that uses the calcium sulfate by-produced here to fix fluorine in wastewater will be provided.
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Abstract
Description
フッ化水素の製造方法 Method for producing hydrogen fluoride
技術分野 Technical field
本発明はフッ化水素の製造方法に関し、 さ らに詳しく はフッ素含 有溶液中のフッ素を有効に利用し、 固体廃棄物の量を削減しうるフ 明 The present invention relates to a method for producing hydrogen fluoride, and more particularly, to a method capable of effectively utilizing fluorine in a fluorine-containing solution to reduce the amount of solid waste.
ッ化水素の製造方法に関する。 The present invention relates to a method for producing hydrogen nitride.
田 Rice field
背景技術 書 Background art
通常、 フッ素含有排水等のフッ素含有溶液の処理は、 生石灰、 消 石灰、 塩化カルシウム等のカルシウム化合物と反応させて、 難溶性 のフッ化カルシゥ ムと して大部分のフッ素を固定化処理した後、 必 要に応じさらにア^/ミニゥム塩法、 フルォロアパタイ ト法、 活性ァ ルミナ法、 塩基性陰イオン交換樹脂法、 A 1 キレー ト樹脂法等の処 理を行なっている。 Usually, the treatment of a fluorine-containing solution such as a fluorine-containing wastewater is performed by reacting with a calcium compound such as quick lime, slaked lime or calcium chloride to fix most of the fluorine as hardly soluble calcium fluoride. If necessary, further treatments such as the aluminium / minium salt method, the fluoroapatite method, the activated alumina method, the basic anion exchange resin method, and the A1 chelate resin method are carried out.
このようにして固定化処理して得られたフッ化カルシウムは、 粒 径が非常に細かく 、 そのままでは濾過できないために凝集剤を用い てフロ ックにし、 ついで沈降分離 ' フィルタープレス濾過を行って いる。 そのため、 水分が 5 0〜 8 0 %もあり、 産業用と して再利用 し難く、 さらには量も大きいためにその処分が問題となっている。 そこで、 生成したフッ化カルシウムスラッジの一部を元に戻し、 種 結晶の役割を持たせることで多少なり とも粒径を大きくすることで 廃棄するスラッジの量を減らしている (たとえば、 「用水と排水」 第 42卷、 第 1 0号、 第 2 7〜 3 2頁 ( 2 0 0 0 ) ) 。 The calcium fluoride obtained by the immobilization treatment in this way has a very fine particle size and cannot be filtered as it is, so it is flocculated using a flocculant, and then subjected to sedimentation separation and filter press filtration. I have. As a result, the water content is as high as 50 to 80%, making it difficult to reuse it for industrial purposes. Therefore, a part of the generated calcium fluoride sludge is returned to its original state, and the amount of sludge to be discarded is reduced by increasing the particle size at least a little by giving a role of seed crystal (for example, Drainage, Vol. 42, No. 10, page 27-32 (2000)).
さらに、 数百 P P mの希薄なフッ素含有溶液については、 フッ化 カルシウムの結晶を成長させて大きな粒径にする方法 (たとえば、 「ク リーンテクノ ロジー」 5月号、 第 4 0〜 4 2頁 ( 2 0 0 1 ) 、 日本工業出版株式会社) もあるが、 スケールの割には処理量が少な いことに加えて、 その回収物の再利用技術が未だ確立されておらず 、 今のところ産業廃棄物と して処理されている。 In addition, for dilute fluorine-containing solutions of several hundred PPm, calcium fluoride crystals are grown to a large particle size (for example, “Clean Technology”, May issue, pp. 40-42 (2001), Nippon Kogyo Publishing Co., Ltd.). The technology for reusing collected materials has not been established yet, and is currently treated as industrial waste.
フッ素の固定化処理で得られたフッ化カルシウム (回収フッ化力 ルシゥム) をフッ化水素製造原料である蛍石と混合して使用する試 みもなされているが、 回収フッ化カルシウムは、 1次粒子の平均粒 径が小さい、 嵩密度が小さい (蛍石の 1 /2〜 1 /4程度) 、 不純物 が多い (特に塩素) 等の問題によ り、 原料乾燥時の粉塵の問題や蛍 石とのなじみが悪く、 製品フッ化水素中の不純物が増加するために ほとんど利用されていない。 Attempts have been made to use calcium fluoride (recovered fluoridation power) obtained by the process of immobilizing fluorine mixed with fluorite, a raw material for hydrogen fluoride production. Due to problems such as small average particle diameter of secondary particles, low bulk density (about 1/2 to 1/4 of fluorite), and high impurities (especially chlorine), there are problems such as It is poorly used with stones and is rarely used because of an increase in impurities in the product hydrogen fluoride.
その中でも、 粒径を大きくするために粒度を揃えた天然炭酸カル シゥムにフッ素含有溶液を通すことにより (C a C 03 + 2 H F→ C a F 2 + H 2 O + C O 2 : 式 ( 1 ) ) 、 天然炭酸カルシウムの骨 格をほとんど保持したままフッ化カルシウムを生成させる試みがな されている (たとえば特開平 6— 6 3 5 6 1号公報) 。 この際、 発 生する炭酸ガスの抜け、 生成するフッ化カルシウムフロ ック、 炭酸 カルシウムの中心部が未反応で残る等の問題があるが、 この方法で 回収フッ化カルシゥムを蛍石と混合して処理した報告 (たとえば新 エネルギー · 産業技術総合開発機構 平成 13年度成果報告書 (平成 13年度地球温暖化防止関連技術開発 「H F C 2 3破壊技術の開発 」 ) ) もされている。 Among them, by passing the fluorine-containing solution naturally carbonate Cal Shiumu having uniform particle size in order to increase the particle size (C a C 0 3 + 2 HF → C a F 2 + H 2 O + CO 2: formula ( 1)), an attempt has been made to produce calcium fluoride while almost maintaining the skeleton of natural calcium carbonate (for example, Japanese Patent Application Laid-Open No. 6-63561). At this time, there are problems such as the escape of generated carbon dioxide gas, the generated calcium fluoride flocks, and the center of calcium carbonate remaining unreacted.However, this method mixes recovered calcium fluoride with fluorite. (For example, the New Energy and Industrial Technology Development Organization 2001 fiscal year report (FY2001 global warming prevention related technology development "Development of HFC23 destruction technology")).
さらに、 石膏に回収フッ化カルシウムを混合。 乾燥して粒径を大 きく して蛍石に混合して使用する方法も提案されている (特表 2 0 0 2 - 5 3 4 3 4 6号公報) 。 発明の開示 本発明の目的は、 排水等の溶液中に存在するフッ素をフッ化カル シゥムと して固定化し、 フッ化水素製造用原料として使用し、 フッ 化水素製造によ り副生した硫酸カルシウムを溶液中のフッ素の固定 化に利用することであり、 これらを組合せることによ りフッ素の固 定化処理に伴う産業廃棄物量をゼロにし得、 同時に資源的に乏しい 天然のフッ化カルシウム (蛍石) を使用しないでフッ素化学産業の キーマテリアルであるフッ化水素を製造し、 ここで副生した硫酸力 ルシゥムを排水中のフッ素の固定化に使用するフッ素リサイクルシ ステムを提供する。 本発明の要旨は、 フッ化水素を製造する際に副 生する硫酸カルシゥムをフッ素含有溶液中のフッ素の固定化に使用 し、 固定化によ り得られたフッ化カルシウムを硫酸と反応させてフ ッ化水素を製造し、 そこで副生する硫酸カルシウムを前記のフッ素 含有溶液中のフッ素の固定化工程に供することを特徴とするフッ化 水素の製造方法にある。 図面の簡単な説明 In addition, the recovered calcium fluoride is mixed with gypsum. A method has also been proposed in which the particles are dried to increase the particle size, and mixed with fluorite for use (Japanese Patent Application Laid-Open No. 2002-53434). Disclosure of the invention An object of the present invention is to fix fluorine present in a solution such as wastewater as calcium fluoride, use it as a raw material for hydrogen fluoride production, and use calcium fluoride produced as a by-product of hydrogen fluoride production as a solution. It is used to fix fluorine in water. By combining these, it is possible to reduce the amount of industrial waste associated with the process of solidifying fluorine to zero, and at the same time, use natural calcium fluoride (fluorite), which is scarce in terms of resources. The company will produce hydrogen fluoride, a key material in the fluorine chemical industry, without using, and provide a fluorine recycling system that uses sulfuric acid as a by-product to fix fluorine in wastewater. The gist of the present invention is that calcium sulfate produced as a by-product in the production of hydrogen fluoride is used for immobilizing fluorine in a fluorine-containing solution, and calcium fluoride obtained by the immobilization is reacted with sulfuric acid. A method for producing hydrogen fluoride, comprising producing hydrogen fluoride, and subjecting the by-produced calcium sulfate to the step of immobilizing fluorine in the fluorine-containing solution. Brief Description of Drawings
図 1は本発明におけるフッ素リサイクルシステムの概念図。 Figure 1 is a conceptual diagram of the fluorine recycling system of the present invention.
図 2は本発明における実施例 (ビーカー試験) に使用したフッ化 水素発生装置を示す。 FIG. 2 shows a hydrogen fluoride generator used in an example (beaker test) of the present invention.
図 3は本発明における実施例 (パイ ロ ッ ト試験) に使用したフ ッ 化水素発生装置を示す。 発明を実施するための最良の形態 FIG. 3 shows a hydrogen fluoride generator used in an embodiment (pilot test) of the present invention. BEST MODE FOR CARRYING OUT THE INVENTION
本発明のフッ化水素の製造方法においては、 フッ化水素を製造す る際に副生する硫酸カルシウムをフッ素含有溶液中のフッ素の固定 化に使用し、 固定化によ り得られたフッ化カルシウムを硫酸と反応 させてフッ化水素を製造し、 そこで副生する硫酸カルシウムを前記 のフッ素含有溶液中のフッ素の固定化工程に供する。 フッ素含有溶 液と しては特に制限されず、 各種の製造プロセスから排出されるフ ッ素含有排水が好適に使用されうる。 In the method for producing hydrogen fluoride of the present invention, calcium sulfate by-produced in producing hydrogen fluoride is used for immobilizing fluorine in a fluorine-containing solution, and the fluoride obtained by the immobilization is used. Hydrogen fluoride is produced by reacting calcium with sulfuric acid. To a step of immobilizing fluorine in a fluorine-containing solution. The fluorine-containing solution is not particularly limited, and fluorine-containing wastewater discharged from various production processes can be suitably used.
フッ素の固定化に使用する硫酸カルシウムは、 無水、 半水もしく は 2水石膏のいずれであってもよい。 .フッ素の固定化反応 (C a S O 4 + 2 F— → C a F 2 + S O 4 2 一 : 式 ( 2 ) ) が塩交換の固一 液反応であり、 しかも硫酸カルシウムの形状を保持したまま反応す るので、 硫酸カルシゥムの平均粒径は 2 0 0 μ m以下であるのが好 適である。 反応後のフッ化カルシウムの純度を高めること と濾過性 を考慮すると 1 0〜2 0 0 /z mが好適であり、 そして 3 0〜; 1 5 0 μ πιがさらに好適である。 しかし、 2 0 0 μ πιを超えてもフッ化力 ルシゥムの含量が低下するだけであり、 次のフッ化水素製造工程に 使用するのに障害にはならない。 The calcium sulfate used for immobilizing fluorine may be anhydrous, hemihydrate or gypsum. . Fluorine immobilization reaction (C a SO 4 + 2 F- → C a F 2 + SO 4 2 one: Equation (2)) is solid one-pack reaction salt exchange, yet retaining the shape of the calcium sulfate Since the reaction proceeds as it is, the average particle size of calcium sulfate is preferably 200 μm or less. In consideration of increasing the purity of the calcium fluoride after the reaction and filterability, 10 to 200 / zm is preferable, and 30 to 150 μπι is more preferable. However, exceeding 200 μπι only decreases the content of fluorinated calcium, and does not hinder use in the next hydrogen fluoride production process.
種々の粒度の無水石膏を用いてフッ化カルシウムへの転換率を比 較すると、 次のような結果が得られた。 すなわち、 篩を用いて各粒 度に分級した無水石膏に対して、 それぞれ 1 . 3倍当量のフッ素を 含有する溶液 (フッ素濃度 1 0, 0 0 Oppm) と室温で 1時間、 攪 拌して反応させたところ、 粒径 2, 0 0 0 μ m以上で転換率 3 7 % ;粒径 2, 0 0 0〜 1 , Ο Ο Ο μ πιで転換率 4 3 % ; 粒径 1 , 0 0 0 〜 5 0 0 μ mで転換率 4 9 % ; 粒径 2 5 0〜 1 6 0 /x mで転換率 8 7 % ; 粒径 1 6 0 μ m以下で転換率 9 2 %であった。 The following results were obtained by comparing the conversion to calcium fluoride using anhydrous gypsum of various particle sizes. That is, a solution containing 1.3 equivalents of fluorine (fluorine concentration: 100,000 ppm) with anhydrous gypsum classified into each particle size using a sieve was stirred at room temperature for 1 hour. After the reaction, the conversion rate was 37% when the particle diameter was 2,000 μm or more; the conversion rate was 43% when the particle diameter was 2,000 to 1, Ο Ομππ; The conversion was 49% at 0 to 500 μm; the conversion was 87% at 250 to 160 / xm; and the conversion was 92% at 160 μm or less.
本発明において得られるフッ化カルシウムは、 沈降性に優れ、 通 常の濾過手段で容易に脱水することができる。 たとえば、 実験室に おける通常の吸引濾過装置を用いて脱水すると、 含水率 2 5〜 3 5 %程度のフッ化カルシウムを得ることができる。 さらに、 遠心脱水 機もしくはフィルタープレスを用いると含水率を 1 5〜2 0 %程度 に容易に低減でき、 通常のフッ素固定化処理で得られている含水率 5 0〜 6 0 %と比較すると半分以下であり うる。 得られるフッ化力 ルシゥムを硫酸と反応させてフッ化水素を製造するに際し、 含水率 4 0 %以下のフッ化カルシウムを用いるのが好適であり、 さ らに好 適には含水率 2 5 %以下である。 The calcium fluoride obtained in the present invention has excellent sedimentation properties, and can be easily dehydrated by ordinary filtration means. For example, when dehydration is performed using a normal suction filtration device in a laboratory, calcium fluoride having a water content of about 25 to 35% can be obtained. Furthermore, the use of a centrifugal dehydrator or a filter press can easily reduce the water content to about 15 to 20%. Compared to 50-60%, it can be less than half. In producing hydrogen fluoride by reacting the resulting fluoridated solution with sulfuric acid, it is preferable to use calcium fluoride having a water content of 40% or less, and more preferably to a water content of 25%. It is as follows.
さらに、 本発明において得られるフッ化カルシウムは、 乾燥後 ( 1 2 0 °C、 2時間) の灼熱減量 ( 5 0 0 °C、 1時間) が、 5 %以下 、 好ましく は 3 %以下、 通常 2 %前後であり、 通常のフッ素固定化 処理で得られているものが 7〜 1 0 %であるのと差異がある。 Further, the calcium fluoride obtained in the present invention has a loss on ignition (500 ° C, 1 hour) after drying (120 ° C, 2 hours) of 5% or less, preferably 3% or less, usually It is around 2%, which is different from that obtained by ordinary fluorine immobilization treatment at 7 to 10%.
このよ うに、 本発明において得られるフッ化カルシウムは、 水分 および灼熱減量が少ないために少ないエネルギーで乾燥でき、 フッ 化水素製造用原料として適している。 Thus, the calcium fluoride obtained in the present invention can be dried with a small amount of energy due to a small amount of water and a small loss on ignition, and is suitable as a raw material for producing hydrogen fluoride.
まず、 嵩比重が蛍石と比較して 1 /2〜 1 /3程度と小さい。 これ は蛍石がほとんど結晶状態であるのに対して、 多孔質なためである 。 このこ とはフッ化水素生成反応 (C a F 2 + H 2 S O 4 → C a S O 4 + 2 H F : 式 ( 3 ) ) の反応性に良好な影響を及ぼす。 First, the bulk specific gravity is about 1/2 to 1/3 smaller than that of fluorite. This is because fluorite is almost crystalline but porous. Hydrogen fluoride generating reaction with Conoco (C a F 2 + H 2 SO 4 → C a SO 4 + 2 HF: Equation (3)) positive effect on the reactivity of the.
フッ化水素製造用原料に使用されている蛍石は、 一般に、 平均粒 径 5 0〜 1 0 0 μ m程度の粉体で飛散防止のために約 1 0 %の水分 を含ませた状態で全量を海外から輸入している。 結晶性のよい蛍石 と硫酸との反応は、 蛍石の表面から徐々に進行し、 生成した硫酸力 ルシゥムで被覆されるために、 十分に混和させた後にロータ リーキ ルンを用いて 4 0 0〜 5 0 0 °Cの温度で、 6〜 8時間かけて行なわ れるのが通常である。 しかしながら、 おおきな粒子は完全には反応 しないで、 芯部にフッ化カルシウムが残ることになる。 Fluorite used as a raw material for the production of hydrogen fluoride is generally a powder having an average particle size of about 50 to 100 μm and containing about 10% water to prevent scattering. The whole amount is imported from overseas. The reaction between fluorite and sulfuric acid with good crystallinity gradually progresses from the surface of the fluorite, and is covered with the generated sulfuric acid. Therefore, the mixture is sufficiently mixed and then mixed with a rotary kiln. It is usually carried out at a temperature of up to 500 ° C. for 6 to 8 hours. However, the large particles do not react completely, leaving calcium fluoride in the core.
一方、 本発明において得られるフッ化カルシウムは多孔質 . 多結 晶体であり、 上記の式 ( 3 ) の反応が円滑に起こるので、 通常 2 0 0 °C、 1時間程度で反応が完結し、 1 5 0 °C以下でも可能である。 このように、 比較的温和な反応条件によ り、 装置材料および反応器 の選択の幅が拡がり、 安価でコンパク トな装置の設計を可能にしう る。 このよ うに、 本発明においては、 固定化によ り得られたフッ化 カルシウムを硫酸と反応させてフッ化水素を製造するに際し、 反応 を通常 2 5 0 °C以下、 好ましく は 1 0 0〜 2 0 0 °Cで行うことがで きる。 使用するフッ化カルシウムの含量は高いほうが好ましいが、 後述するよ うに含量 6 0 %程度でも不純物の大部分が硫酸カルシゥ ムであるので問題がない。 On the other hand, the calcium fluoride obtained in the present invention is a porous and polycrystalline substance, and the reaction of the above formula (3) occurs smoothly. Therefore, the reaction is usually completed in about 200 ° C. for about 1 hour. It is possible even below 150 ° C. As described above, the relatively mild reaction conditions cause the equipment materials and reactor The range of choices will be expanded, and it will be possible to design inexpensive and compact equipment. Thus, in the present invention, when the calcium fluoride obtained by the immobilization is reacted with sulfuric acid to produce hydrogen fluoride, the reaction is usually carried out at a temperature of 250 ° C. or lower, preferably 100 ° C. or less. It can be performed at 200 ° C. It is preferable that the content of calcium fluoride used is higher, but there is no problem even if the content is about 60%, as described later, since most of the impurities are calcium sulfate.
さ らに、 式 ( 2 ) の反応によ り得られたフッ化カルシウムは、 蛍 石の主要不純物であるシリカ分をほとんど含有しないので、 問題と なる副生ケィフッ化水素酸を生成しない利点も有する。 Furthermore, the calcium fluoride obtained by the reaction of the formula (2) hardly contains silica, which is a major impurity of fluorite, and therefore has the advantage of not producing the problematic by-product ky hydrofluoric acid. Have.
使用する硫酸としては発煙硫酸、 または発煙硫酸と硫酸の混合物 が挙げられ、 硫酸の量はフッ化カルシウムの含量に比例するが、 フ ッ化カルシウム量に対し当量以下の硫酸を用いるのが好適である。 過剰量の硫酸は生成した硫酸カルシウム中に残留するため無駄とな り好ましく ない。 一方、 当量よ り少ないと未反応のフッ化カルシゥ ムが残るが、 次のフッ素の固定化に供しう る。 フッ化水素の回収率 および装置の耐食性を高めるために、 反応系に存在する水分を極力 避けるのが好ましい。 このため硫酸中の水分とフッ化カルシウムの 灼熱減量に相当する水分量に見合う発煙硫酸を使用するか、 もしく は予め発煙硫酸と硫酸を混合して 1 0 %程度の発煙硫酸を調製して おくのが好適である。 このよ うに、 本発明においてはフッ化カルシ ゥム量に対し当量〜 0 . 8倍当量の硫酸を用いるのが最も好適であ る。 The sulfuric acid to be used is fuming sulfuric acid or a mixture of fuming sulfuric acid and sulfuric acid.The amount of sulfuric acid is proportional to the content of calcium fluoride, but it is preferable to use sulfuric acid having an equivalent amount or less with respect to the amount of calcium fluoride. is there. An excessive amount of sulfuric acid remains in the generated calcium sulfate and is not preferable because it is wasted. On the other hand, if the amount is less than the equivalent, unreacted calcium fluoride remains, but it is used for the next immobilization of fluorine. In order to increase the recovery rate of hydrogen fluoride and the corrosion resistance of the apparatus, it is preferable to minimize the amount of water present in the reaction system. Therefore, use fuming sulfuric acid that matches the amount of water in the sulfuric acid and the water loss corresponding to the ignition loss of calcium fluoride, or prepare a fuming sulfuric acid of about 10% by mixing fuming sulfuric acid and sulfuric acid in advance. It is preferable to keep it. As described above, in the present invention, it is most preferable to use sulfuric acid in an amount equivalent to 0.8 times the amount of calcium fluoride.
この反応で副生する硫酸カルシウムを主成分とする固形分は、 フ ッ素含有溶液中のフッ素の固定化処理に使用するために、 平均粒径 2 0 0 μ m以下に粉砕するのが好ましい。 粉砕は乾式、 湿式のいず れであってもよい。 また、 反応性を高めるために、 消石灰、 水酸化 ナトリ ウム等のアルカ リ性物質を添加してフッ素含有溶液の p Hを 5〜 9に調整するのが好適である。 The solid content mainly composed of calcium sulfate by-produced in this reaction is preferably pulverized to an average particle diameter of 200 μm or less in order to use the solid content of fluorine in a fluorine-containing solution. . The pulverization may be either dry or wet. Also, to increase reactivity, slaked lime, hydroxylated It is preferable to adjust the pH of the fluorine-containing solution to 5 to 9 by adding an alkaline substance such as sodium.
以上のように、 本発明によれば、 フッ化水素製造時に副生する硫 酸カルシウムをフッ素含有溶液中のフッ素の固定化に使用し、 ここ で得られたフッ化カルシウムを硫酸と反応させてフッ化水素を製造 し、 副生した硫酸カルシウムを上記のフッ素含有溶液中のフッ素の 固定化に使用するフッ素リサイクルシステムを提供しう る。 その概 要を図 1に示す。 As described above, according to the present invention, calcium sulfate by-produced during the production of hydrogen fluoride is used for immobilizing fluorine in a fluorine-containing solution, and the calcium fluoride obtained here is reacted with sulfuric acid. Provided is a fluorine recycling system for producing hydrogen fluoride and using the by-produced calcium sulfate for immobilizing fluorine in the above-mentioned fluorine-containing solution. Figure 1 shows the outline.
さらに、 本発明においては、 硫酸カルシウムをフッ素含有溶液と 混合して、 該溶液中のフッ素をフッ化カルシウムと して固定化して 回収する方法において、 硫酸カルシゥムの粒径が 1 0〜2 0 0 μ πι であり、 かつフッ素に対する硫酸カルシウムにおけるカルシウムの モル比 ( M c a / 2 M F ) (ここで、 M c a /はカルシウムのモル数 ; M F はフッ素のモル数) 力 S O . 8以上、 1 . 2未満であることを 特徴とする。 モル比は好適には 0 . 8以上、 1 . 1未満である。 Further, in the present invention, in the method of mixing calcium sulfate with a fluorine-containing solution and fixing and recovering fluorine in the solution as calcium fluoride, the calcium sulfate has a particle diameter of 10 to 200. μ is Paiiota, and the molar ratio of calcium in the calcium sulfate to fluorine (M ca / 2 M F) ( wherein, M ca / the number of moles of calcium; M F is the number of moles of fluorine). force SO 8 or more, Less than 1.2. The molar ratio is preferably at least 0.8 and less than 1.1.
このよ うな構成を揉用するこ とによ り、 各種のフッ素含有溶液か らフッ素を粒径が比較的大きく濾過性が良好なフッ化カルシウムと して固定化して回収しうる。 この方法は得られるフッ化カルシウム をフッ化水素の製造に使用しないで、 中空糸膜、 フィルタープレス 等の膜を使用して回収する場合に特に有用である。 By rubbing such a configuration, fluorine can be recovered from various fluorine-containing solutions by immobilizing it as calcium fluoride having a relatively large particle size and good filterability. This method is particularly useful when the obtained calcium fluoride is not used for the production of hydrogen fluoride but is recovered using a membrane such as a hollow fiber membrane or a filter press.
以下, 実施例により本発明をさ らに詳細に説明するが、 本発明は これらの実施例に限定されない。 Hereinafter, the present invention will be described in more detail with reference to Examples, but the present invention is not limited to these Examples.
実施例 1 Example 1
フッ酸製造ブラン トにおいて副生した無水石膏を粉砕したもの ( 平均粒径 6 5 μ πι ) 1, 0 0 0 g と無機フッ化物合成排水 (フッ素 濃度 8, 8 0 0 ppm) 4 0 k gを、 攪拌器を備えた 5 0 Lのポリェチ レン製反応容器に入れ、 1時間攪拌後、 暫く固形物を沈降させた後 、 上澄み液を除き、 吸引濾過器を用いて脱水し、 固形物 8 2 0 gを 回収した。 1 2 0 °Cに設定した温風乾燥機にて 2時間乾燥後 (乾燥 減量 2 6. 5 %) して、 固形物 (灼熱減量 1. 7 %、 フッ化カルシ ゥム含量 8 7. 8 %、 硫酸カルシウム含量 1 0. 5 %) 6 0 3 gを 得た。 この際、 処理水のフッ素濃度は 1, 7 0 0 ppmに下がってい た。 Anhydrous gypsum produced as a by-product in a hydrofluoric acid production brand was pulverized (average particle size: 65 μπι) (100 g) and inorganic fluoride synthetic wastewater (fluorine concentration: 8,800 ppm) (40 kg). , Placed in a 50 L polyethylene reaction vessel equipped with a stirrer, stirred for 1 hour, and settled solids for a while Then, the supernatant was removed, and the mixture was dehydrated using a suction filter to collect 820 g of a solid. After drying in a warm air dryer set at 120 ° C for 2 hours (loss on drying 26.5%), solid matter (loss on ignition 1.7%, calcium fluoride content 87.8) %, Calcium sulfate content: 10.5%). At this time, the fluorine concentration of the treated water had dropped to 1,700 ppm.
実施例 2 Example 2
実施例 1で得た固形物 (灼熱減量 1. 7 %、 フッ化カルシウム含 量 8 7. 8 %、 硫酸カルシウム含量 1 0. 5 %) 2 5 0. 5 gを図 2のフッ素樹脂 P F A製の容器 ( 1 ) に入れ、 反応器に入れたフッ 化カルシウムの理論量に相当する 9 8 %硫酸 2 8 5. 9 gをフッ素 樹脂 P F A製の硫酸滴下ロー ト ( 2 ) に秤取り、 図 2に示すように セッ ト した ( Aはフッ化カルシウム、 Bは硫酸、 Cはシリ コンオイル 、 そして Dは氷/食塩) 。 硫酸をゆつく り滴下し、 硫酸がフッ化カル シゥムと十分に馴染んだことを確認してから、 徐々にオイルパス ( 3 ) の温度を上げ、 3時間かけて 1 8 0 °Cまで昇温させた ( ( 4 ) はフッ素樹脂 P F A製冷却器) 。 この時点で反応は完結しており、 20.5 g of the solid obtained in Example 1 (ignition loss 1.7%, calcium fluoride content 87.8%, calcium sulfate content 10.5%) was made from the fluororesin PFA shown in Fig. 2. Weighs 98.85 g of 98% sulfuric acid, equivalent to the theoretical amount of calcium fluoride placed in the reactor, into a sulfuric acid dropping funnel (2) made of fluororesin PFA. They were set as shown in Figure 2 (A for calcium fluoride, B for sulfuric acid, C for silicon oil, and D for ice / saline). Sulfuric acid is slowly dropped, and after confirming that the sulfuric acid has become fully compatible with calcium fluoride, gradually raise the temperature of the oil path (3) and raise the temperature to 180 ° C over 3 hours. ((4) is a fluorine resin PFA cooler). At this point the reaction is complete,
9 2. 5 gのフッ化水素がフッ素榭脂 P F A製のフッ化水素回収ト ラップ ( 5 ) に溜まっていた (回収収率 8 2. 2 %) ( ( 6 ) はデ ュヮー瓶) 。 反応容器を冷却後、 中から固形物 4 3 3. 9 gを回収 した。 92.5 g of hydrogen fluoride was collected in a hydrogen fluoride recovery trap (5) made of fluororesin PFA (recovery yield: 82.2%) ((6) is a Duty bottle). After cooling the reaction vessel, 43.3.9 g of solid matter was recovered from inside.
回収した固形物をすりつぶして 2 0 0 μ m以下にし、 その内 3 5 3. 2 g と無機フッ化物合成排水 (フッ素濃度 1 2 , 0 0 Oppm) The collected solids are ground to 200 μm or less, of which 353.2 g and inorganic fluoride synthetic wastewater (fluorine concentration of 12,200 ppm)
1 0 k gを 1 0 Lの攪拌器を備えたポリエチレン製反応容器に入れ て攪拌した。 スラ リ ー液の p Hを中性にするために 2 5. 1 %の水 酸化ナト リ ウム水溶液を 8 1. 5 g加えた。 1時間後、 攪拌を止め て暫く 固形物を沈降させた後、 上澄液を除き、 吸引濾過器を用いて 脱水し、 固形物 3 3 7. 8 gを回収した。 1 2 0 °Cに設定した温風 乾燥機にて 2時間乾燥 (乾燥減量 3 2. 1 %) して固形物 (灼熱減 量 2. 1 %、 フッ化カルシウム含量 9 0. 8 %、 硫酸カルシウム含 量 7. 1 %) 2 2 9. 3 gを得た。 10 kg was placed in a polyethylene reaction vessel equipped with a 10 L stirrer and stirred. To make the pH of the slurry solution neutral, 81.5 g of a 25.1% aqueous sodium hydroxide solution was added. After 1 hour, stop stirring and allow the solid to settle for a while, then remove the supernatant and use a suction filter. After dehydration, 37.8 g of a solid was recovered. Dry in a warm air dryer set at 120 ° C for 2 hours (loss on drying 32.1%) and solid (loss on ignition 2.1%, calcium fluoride content 90.8%, sulfuric acid) (Calcium content 7.1%) 29.3 g was obtained.
実施例 3 Example 3
実施例 2 と同様の方法で回収した固形物をすりつぶさないで同様 にフッ素の固定化を行った。 得られた固形物中のフッ化カルシウム 含量は 5 6 %であった。 The solid matter recovered in the same manner as in Example 2 was similarly immobilized with fluorine without being ground. The calcium fluoride content in the obtained solid was 56%.
実施例 4 Example 4
フッ化カルシウム含量の低い固形物 (灼熱減量 2. 3 %、 フッ化 カルシウム含量 5 8. 0 %、 硫酸カルシウム含量 3 9. 7 %) 3 0 0. 1 gをフッ素樹脂 P F A製の容器に入れ、 反応器に入れたフッ 化カルシウムの理論量に相当する 9 8 %硫酸 2 3 3. 3 gをフッ素 樹脂 P F A製の硫酸滴下ロートに秤取り、 図 2に示すようにセッ ト した。 硫酸をゆっく り滴下し、 硫酸がフッ化カルシウムと十分に馴 染んだことを確認してから、 徐々にオイルパスの温度を上げ、 3時 間かけて 1 8 0 °Cまで昇温させた。 この時点で反応は完結しており 、 5 8. 9 gのフッ化水素がフッ素樹脂 P F A製のフッ化水素回収 トラップに溜まっていた (回収収率 6 6. 1 %) 。 反応容器を冷却 後、 中から固形物 4 6 0. 5 gを回収した。 Solids with low calcium fluoride content (2.3% loss on ignition, 58.0% calcium fluoride content, 39.7% calcium sulfate content) 30.1 g of 30.1 in a fluoroplastic PFA container Then, 233.3 g of 98% sulfuric acid corresponding to the theoretical amount of calcium fluoride placed in the reactor was weighed into a sulfuric acid dropping funnel made of fluororesin PFA and set as shown in FIG. Sulfuric acid is slowly added dropwise, and after confirming that the sulfuric acid has become sufficiently compatible with the calcium fluoride, gradually raise the temperature of the oil path and raise the temperature to 180 ° C over 3 hours. Was. At this point, the reaction was completed, and 58.9 g of hydrogen fluoride had accumulated in the hydrogen fluoride recovery trap made of fluororesin PFA (recovery yield: 66.1%). After cooling the reaction vessel, 460.5 g of a solid substance was recovered from the inside.
回収した固形物をすりつぶして 2 0 0 μ πι以下にし、 その内 3 5 0. 1 g と無機フッ化物合成排水 (フッ素濃度 1 2 , 0 0 0 ppm) 1 0 k gを 1 0Lの攪拌器を備えたポリエチレン製反応容器に入れ て攪拌した。 スラ リー液の p Hを中性にするために 2 5. 1 %の水 酸化ナト リ ウム水溶液を 9 2. 0 g加えた。 1時間後、 攪拌を止め て暫く 固形物を沈降させた後、 上澄液を除き、 吸引濾過器を用いて 脱水し、 固形物 3 7 5. l gを回収した。 1 2 0 °Cに設定した温風 乾燥機にて 2時間乾燥 (乾燥減量 2 8. 2 %) して固形物 (灼熱減 量 2. 3 %、 フッ化カルシウム含量 9 1. 6 %、 硫酸カルシウム含 量 7. 1 %) 2 6 9. 2 gを得た。 Grind the collected solids to less than 200 μππι, and add 350.1 g of the solid waste and 10 kg of inorganic fluoride synthetic wastewater (fluorine concentration of 12,200 ppm) to a 10 L stirrer. The mixture was stirred in a polyethylene reaction vessel provided. To make the pH of the slurry solution neutral, 92.0 g of a 25.1% aqueous sodium hydroxide solution was added. After 1 hour, the stirring was stopped to allow a solid to settle for a while, then the supernatant was removed, and the solid was dehydrated using a suction filter to collect 377.5 lg of the solid. Warm air set at 120 ° C Dry in a dryer for 2 hours (loss on drying 28.2%) and solid matter (loss on ignition 2.3%, content of calcium fluoride 91.6%, content of calcium sulfate 7.1%) 26 9.2 g were obtained.
実施例 5 Example 5
実施例 1で得た固形物 (灼熱減量 1. 7 %、 フッ化カルシウム含 量 8 7. 8 %、 硫酸カルシウム含量 1 0. 5 %) 2 5 2. 3 gをフ ッ素樹脂 P F A製の容器に入れ、 反応器に入れたフッ化カルシウム の理論量に相当する 5 %発煙硫酸 (硫酸と 2 5 %発煙硫酸を混ぜて 調製したもの) 2 7 8. 3 gをフッ素樹脂 P F A製の硫酸滴下ロー トに秤取り、 図 2に示すようにセッ トした。 5 %発煙硫酸をゆつく り滴下し、 硫酸がフッ化カルシウムと十分に馴染んだことを確認し てから、 徐々にオイルパスの温度を上げ、 3時間かけて 1 8 0 °Cま で昇温させた。 この時点で反応は完結しており、 1 0 5. 2 gのフ ッ化水素がフッ素樹脂 P F A製のフッ化水素回収トラップに溜まつ ていた (回収収率 9 2. 6 %) 。 反応容器を冷却後、 中から固形物 4 1 8. 9 gを回収した。 252.3 g of the solid obtained in Example 1 (lost loss of 1.7%, calcium fluoride content of 87.8%, calcium sulfate content of 10.5%) was prepared from a fluororesin PFA. 5% fuming sulfuric acid (prepared by mixing sulfuric acid and 25% fuming sulfuric acid) equivalent to the theoretical amount of calcium fluoride put in a vessel and placed in a reactor 27.8.3 g of sulfuric acid made of fluoroplastic PFA It was weighed on a dropping funnel and set as shown in Fig.2. Slowly add 5% fuming sulfuric acid, and after confirming that sulfuric acid has become sufficiently compatible with calcium fluoride, gradually raise the temperature of the oil path and raise the temperature to 180 ° C over 3 hours. I let it. At this point, the reaction was completed, and 105.2 g of hydrogen fluoride had accumulated in the hydrogen fluoride recovery trap made of fluororesin PFA (recovery yield 92.6%). After cooling the reaction vessel, 418 g of a solid was recovered from the inside.
回収した固形物をすりつぶして 2 0 0 μ ηι以下にし、 その内 3 5 0. 6 g と無機フッ化物合成排水 (フッ素濃度 1 2, 0 0 Oppm) 1 0 k gを 1 0Lの攪拌器を備えたポリエチレン製反応容器に入れ て攪拌した。 スラリー液の p Hを中性にするために 2 5. 1 %の水 酸化ナト リ ウム水溶液を 2 0. 4 g加えた。 1時間後、 攪拌を止め て暫く固形物を沈降させた後、 上澄液を除き、 吸引濾過器を用いて 脱水し、 固形物 2 8 7. 2 gを回収した。 1 2 0 °Cに設定した温風 乾燥機にて 2時間乾燥 (乾燥減量 2 6. 8 %) して固形物 (灼熱減 量 2. 1 %、 フッ化カルシウム含量 9 1 . 6 %、 硫酸カルシウム含 量 6. 3 %) 2 1 0. 2 gを得た。 Grind the collected solid to 200 μηη or less, and equip it with 350.6 g and 10 kg of inorganic fluoride synthetic wastewater (fluorine concentration 12, 00 Oppm) with 10 L of stirrer. And stirred in a polyethylene reaction vessel. To make the pH of the slurry liquid neutral, 20.4 g of a 25.1% aqueous sodium hydroxide solution was added. One hour later, stirring was stopped to allow a solid to settle for a while, then the supernatant was removed, and the solid was dehydrated using a suction filter to collect 287.2 g of a solid. Dry in a warm air dryer set at 120 ° C for 2 hours (loss on drying 26.8%) and solid matter (loss on burning 2.1%, calcium fluoride content 91.6%, sulfuric acid) (Calcium content 6.3%) 20.2 g was obtained.
実施例 6 硫酸カルシウムと無機フッ素化合物合成排液の処理により得られ た固形物 (灼熱減量 1 . 8 %、 フッ化カルシウム含量 9 1. 2 %、 硫酸カルシウム含量 7. 0 %) 7, 0 0 3 gを攪拌機、 スチームジ ャケッ ト、 温度計等を備えたハステロィ C 2 2製の 1 0 L反応容器 ( 1 1 ) に入れ、 反応容器に入れたフッ化カルシウムの理論量に相 当する 5 %発煙硫酸 (硫酸と 2 5 %発煙硫酸を混ぜて調製したもの ) 8, 0 3 4 gをフッ素樹脂 P F A製の硫酸滴下ロー ト ( 1 2 ) に 秤取り、 図 3に示すよ うにセッ ト した (Aはフッ化カルシウム、 Bは 硫酸) 。 攪拌しながら 5 %発煙硫酸をゆつく り滴下した後、 ジャケ ッ ト部 ( 1 3 ) にスチームを流して徐々に温度を上げた。 約 3時間 かけて内温を 1 5 0 °Cまで昇温させた ( ( 1 4 ) は SUS 3 1 6製冷 却器) 。 この時点で反応は完結しており、 2, 9 9 7 gのフッ化水 素が S U S 3 1 6製のフッ化水素回収トラップ ( 1 5 ) に溜まって いた (回収収率 9 1. 5 %) 。 反応容器を冷却後、 中から固形物 1 1, 9 2 2 gを回収した。 Example 6 7,003 g of solid matter obtained by treating calcium sulfate and inorganic fluorine compound synthetic wastewater (loss on ignition 1.8%, calcium fluoride content 91.2%, calcium sulfate content 7.0%) Put into a Hastelloy C22 10 L reaction vessel (11) equipped with a stirrer, steam jacket, thermometer, etc., and add 5% fuming sulfuric acid equivalent to the theoretical amount of calcium fluoride put in the reaction vessel (11%). (Prepared by mixing sulfuric acid and 25% fuming sulfuric acid) 8,034 g was weighed into a sulfuric acid dropping funnel (12) made of fluororesin PFA, and set as shown in Fig. 3 (A is Calcium fluoride, B is sulfuric acid). After slowly dropping 5% fuming sulfuric acid with stirring, steam was flowed through the jacket (13) to gradually raise the temperature. The internal temperature was raised to 150 ° C over about 3 hours ((14) is a SUS316 cooler). At this point, the reaction was completed and 2,997 g of hydrogen fluoride had accumulated in the SUS316 hydrogen fluoride recovery trap (15) (recovery yield: 91.5%). ). After cooling the reaction vessel, 11, 922 g of solid matter was recovered from the inside.
回収した固形物をすりつぶして 2 0 0 μ πι以下にし、 その全量を 無機フッ化物合成排水 (フッ素濃度 1 2, 0 0 0 ppm) 3 0 0 Lを 5 0 0 Lの攪拌器を備えたポリエチレン製反応容器に入れて攪拌し た。 スラ リー液の p Hを中性にするために 2 0 %の水酸化カルシゥ ム水溶液を 6 7 0 g加えた。 1時間後、 攪拌を止めて暫く固形物を 沈降させた後、 上澄液を除き、 吸引濾過器を用いて脱水し、 固形物 8, 4 9 8 gを回収した。 1 2 0 °Cに設定した温風乾燥機にて 2時 間乾燥 (乾燥減量 1 7. 5 %) して固形物 (灼熱減量 2. 3 %、 フ ッ化カルシウム含量 9 1. 5 %、 硫酸カルシウム含量 7. 2 %) 7 , 0 1 1 gを得た。 The collected solid is ground to 200 μππ or less, and the entire amount is made up of inorganic fluoride synthetic wastewater (fluorine concentration: 12,100 ppm). And stirred. To make the pH of the slurry solution neutral, 670 g of a 20% aqueous calcium hydroxide solution was added. One hour later, the stirring was stopped to allow a solid to settle for a while, and then the supernatant was removed, followed by dehydration using a suction filter to recover 8,498 g of the solid. Dry in a warm air dryer set at 120 ° C for 2 hours (loss on drying 17.5%) and solid matter (loss on burning 2.3%, calcium fluoride content 91.5%, (Calcium sulfate content 7.2%) 7,011 g was obtained.
実施例 7 ' Example 7 '
実施例 6で得られた固形物 (灼熱減量 2. 3 °/。、 フッ化カルシゥ ム含量 9 1. 5 %、 硫酸カルシウム含量 7. 2 %) 6 , 9 9 8 gを 攪拌機、 スチームジャケッ ト、 温度計等を備えたハステロィ C 2 2 製の 1 0 L反応容器に入れ、 反応容器に入れたフッ化カルシウムの 理論量に相当する 5 %発煙硫酸 (硫酸と 2 5 %発煙硫酸を混ぜて調 製したもの) 8 , 0 4 5 gをフッ素樹脂 P F A製の硫酸滴下ロート に秤取り、 図 3に示すよ うにセッ ト した。 攪拌しながら 5 %発煙硫 酸をゆつく り滴下した後、 ジャケッ ト部にスチームを流して徐々に 温度を上げた。 約 3時間かけて内温を 1 5 0 °Cまで昇温させた。 こ の時点で反応は完結しており、 2, 9 6 9 gのフッ化水素が S U S 3 1 6製のフッ化水素回収トラップに溜まっていた (回収収率 9 0 . 3 %) 。 反応容器を冷却後、 中から固形物 1 1, 9 0 8 gを回収 した。 The solid obtained in Example 6 (ignition loss 2.3 ° /., Calcium fluoride) (91.5%, calcium sulfate content 7.2%) 6, 998 g was placed in a 10 L reaction vessel made of Hastelloy C22 equipped with a stirrer, steam jacket, thermometer, etc., and reacted. 5% fuming sulfuric acid (prepared by mixing sulfuric acid and 25% fuming sulfuric acid) corresponding to the theoretical amount of calcium fluoride in a container 8,045 g was weighed into a sulfuric acid dropping funnel made of fluoroplastic PFA. And set as shown in Figure 3. After slowly dropping 5% fuming sulfuric acid with stirring, steam was flowed through the jacket to gradually raise the temperature. The internal temperature was raised to 150 ° C. over about 3 hours. At this point, the reaction was completed, and 2,969 g of hydrogen fluoride had accumulated in the SUS316 hydrogen fluoride recovery trap (recovery yield: 90.3%). After cooling the reaction vessel, 11,908 g of solid matter was recovered from inside.
回収した固形物をすりつぶして 2 0 0 μ πι以下にし、 その全量を 無機フッ化物合成排水 (フッ素濃度 1 2 , 0 0 0 ppm) 3 0 0 Lを 5 0 0 Lの攪拌器を備えたポリエチレン製反応容器に入れて攪拌し た。 スラリー液の p Hを中性にするために 2 0 %の水酸化カルシゥ ム水溶液を 7 1 2 g加えた。 1時間後、 攪拌を止めて暫く固形物を 沈降させた後、 上澄液を除き、 吸引濾過器を用いて脱水し、 固形物 8 , 4 1 6 gを回収した。 1 2 0 °Cに設定した温風乾燥機にて 2時 間乾燥 (乾燥減量 1 6. 8 %) して固形物 (灼熱減量 2. 0 %、 フ ッ化カルシウム含量 9 2. 2 %、 硫酸カルシウム含量 5. 8 %) 7 , 0 0 2 gを得た。 産業上の利用の可能性 The collected solid is ground to 200 μππ or less, and the entire amount is made up of inorganic fluoride synthetic wastewater (fluorine concentration: 12,100 ppm). And stirred. To make the pH of the slurry liquid neutral, 712 g of a 20% aqueous calcium hydroxide solution was added. After 1 hour, stirring was stopped to allow a solid to settle for a while, then the supernatant was removed, and dehydration was performed using a suction filter to recover 8,416 g of the solid. Dry in a warm air dryer set at 120 ° C for 2 hours (loss on drying 16.8%), and solid matter (loss on burning 2.0%, calcium fluoride content 92.2%, (Calcium sulfate content: 5.8%) 7,002 g was obtained. Industrial potential
本発明によれば、 溶液中のフッ素の固定化処理を効率的に行ない 、 同時に資源的に乏しい天然のフッ化カルシウム (蛍石) を使用し ないでフッ素化学産業のキーマテリ アルであるフッ化水素を製造し 、 ここで副生した硫酸カルシウムを排水中のフッ素の固定化に使用 するフッ素リサイクルシステムを提供しう る。 According to the present invention, hydrogen fluoride, which is a key material of the fluorine chemical industry, is capable of efficiently immobilizing fluorine in a solution and not using natural calcium fluoride (fluorite) which is scarce in resources. Manufacture Here, a fluorine recycling system that uses the calcium sulfate by-produced here to fix fluorine in wastewater will be provided.
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| JP2004005493A JP2005200233A (en) | 2004-01-13 | 2004-01-13 | Method for producing hydrogen fluoride |
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Cited By (2)
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| CN108910825A (en) * | 2018-07-27 | 2018-11-30 | 烟台中瑞化工有限公司 | A kind of feed intake consersion unit and reaction method that feeds intake preparing hydrogen fluoride |
| CN115338238A (en) * | 2022-08-16 | 2022-11-15 | 甘肃润源环境资源科技有限公司 | Fluorine-fixing agent and method for aluminum electrolytic cell |
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| JP4652948B2 (en) * | 2005-10-21 | 2011-03-16 | 森田化学工業株式会社 | Method for producing hydrogen fluoride using recovered calcium fluoride |
| EP2118000B1 (en) * | 2007-02-02 | 2011-05-25 | Solvay Fluor GmbH | Preparation of hydrogen fluoride from calcium fluoride and sulfuric acid |
| EP2268573A1 (en) * | 2008-04-22 | 2011-01-05 | Solvay Fluor GmbH | Preparation of hydrogen fluoride from fluorspar or calcium fluoride containing waste material |
| CN105217576B (en) * | 2015-10-28 | 2017-12-01 | 浙江东瓯过滤机制造有限公司 | Filtration washing control method in hydrogen fluoride preparation technology |
| CN109225060B (en) * | 2018-10-17 | 2020-10-02 | 苏州知瑞光电材料科技有限公司 | Use method of special filter material granulation device for preparing hydrogen fluoride moving bed filter |
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| JPS49122880A (en) * | 1973-03-28 | 1974-11-25 | ||
| JPH06262170A (en) * | 1993-03-11 | 1994-09-20 | Nec Corp | Treatment of fluorine-containing waste water |
| JP2004000846A (en) * | 2002-05-31 | 2004-01-08 | Sadaaki Murakami | Fluorine-containing water treatment method |
-
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- 2004-01-13 JP JP2004005493A patent/JP2005200233A/en not_active Withdrawn
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| Publication number | Priority date | Publication date | Assignee | Title |
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| JPS49122880A (en) * | 1973-03-28 | 1974-11-25 | ||
| JPH06262170A (en) * | 1993-03-11 | 1994-09-20 | Nec Corp | Treatment of fluorine-containing waste water |
| JP2004000846A (en) * | 2002-05-31 | 2004-01-08 | Sadaaki Murakami | Fluorine-containing water treatment method |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN108910825A (en) * | 2018-07-27 | 2018-11-30 | 烟台中瑞化工有限公司 | A kind of feed intake consersion unit and reaction method that feeds intake preparing hydrogen fluoride |
| CN108910825B (en) * | 2018-07-27 | 2022-10-18 | 烟台中瑞化工有限公司 | Feeding reaction equipment and feeding reaction method for preparing hydrogen fluoride |
| CN115338238A (en) * | 2022-08-16 | 2022-11-15 | 甘肃润源环境资源科技有限公司 | Fluorine-fixing agent and method for aluminum electrolytic cell |
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