WO2015080095A1 - Method for regenerating molten salt for chemical reinforcement of glass - Google Patents
Method for regenerating molten salt for chemical reinforcement of glass Download PDFInfo
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- WO2015080095A1 WO2015080095A1 PCT/JP2014/081085 JP2014081085W WO2015080095A1 WO 2015080095 A1 WO2015080095 A1 WO 2015080095A1 JP 2014081085 W JP2014081085 W JP 2014081085W WO 2015080095 A1 WO2015080095 A1 WO 2015080095A1
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- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03C—CHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
- C03C21/00—Treatment of glass, not in the form of fibres or filaments, by diffusing ions or metals in the surface
- C03C21/001—Treatment of glass, not in the form of fibres or filaments, by diffusing ions or metals in the surface in liquid phase, e.g. molten salts, solutions
- C03C21/002—Treatment of glass, not in the form of fibres or filaments, by diffusing ions or metals in the surface in liquid phase, e.g. molten salts, solutions to perform ion-exchange between alkali ions
Definitions
- the present invention relates to a method for regenerating a molten salt used for chemical strengthening treatment, and particularly to a method for regenerating a molten salt containing potassium nitrate.
- Cover glass of display devices such as digital cameras, mobile phones, and PDAs (Personal Digital Assistants), and glass substrates of displays are sometimes referred to simply as “chemically tempered glass” glass that has been chemically strengthened by ion exchange or the like. .) Is used.
- Chemical strengthening treatment by ion exchange compresses the glass surface by substituting metal ions with a small ionic radius (for example, Na ions) and metal ions with a larger ionic radius (for example, K ions) contained in the glass. This is a process for generating a stress layer and improving the strength of the glass.
- metal ions with a small ionic radius for example, Na ions
- metal ions with a larger ionic radius for example, K ions
- the molten salt in which the desired CS value cannot be obtained by the chemical strengthening treatment is usually allowed to cool and solidify, and then ground into small blocks and discarded.
- waste molten salt (waste salt) cannot be used again, but there existed problems, such as having to use a large amount of molten salt. Therefore, in Patent Document 1, it is assumed that Li or Cs in the glass component is mixed as an impurity in the molten salt, and that the ion exchange capacity of the molten salt is reduced.
- a method of regenerating a molten salt by allowing it to fall into water as a shower and dissolving, cooling and separating the molten salt in the water is disclosed.
- an object of the present invention is to provide a method for regenerating a molten salt for glass chemical strengthening treatment that has little influence on glass performance.
- the present inventors dissolved the molten salt (waste salt) used in the chemical strengthening treatment in an aqueous solution at a temperature lower than the melting point, cooled and dried, thereby reducing the Na concentration. Only the salt can be taken out, and it has been found that the salt having a low Na concentration can be used again as a molten salt for chemical strengthening treatment of glass, and the present invention has been completed.
- the present invention relates to the following ⁇ 1> to ⁇ 6>.
- ⁇ 1> A method for regenerating a molten salt for glass chemical strengthening, the step of dissolving the molten salt after glass chemical strengthening treatment in water at a temperature lower than the melting point of the molten salt, and cooling the aqueous solution obtained in the melting step
- a method for regenerating a molten salt for strengthening glass chemistry comprising a step of obtaining a regenerated salt and a step of drying to reduce the water content in the regenerated salt to less than 5% by mass.
- ⁇ 2> The method for regenerating a molten salt for strengthening glass chemistry according to ⁇ 1>, wherein the step of cooling the aqueous solution to obtain a regenerated salt further includes a step of concentrating the aqueous solution.
- ⁇ 3> The method for regenerating a molten salt for glass chemical strengthening according to ⁇ 1> or ⁇ 2>, wherein the molten salt for glass chemical strengthening includes potassium nitrate.
- ⁇ 4> The method for regenerating a molten salt for glass chemical strengthening according to any one of ⁇ 1> to ⁇ 3>, wherein a moisture content in the regenerated salt is less than 0.2% by mass in the drying step.
- ⁇ 5> In the step of cooling the aqueous solution to obtain a regenerated salt, the cooled solution is solid-liquid separated into a regenerated salt and a filtrate, and a part of the filtrate is mixed with the solution in the dissolution step, ⁇ 1
- ⁇ 6> The regenerated salt obtained by the solid-liquid separation is washed, further solid-liquid separated into a regenerated salt and a filtrate, and a part of the filtrate is mixed with the dissolved solution in the dissolving step.
- a part of the molten salt (waste salt) after the chemical strengthening treatment that has been conventionally discarded can be used again for the chemical strengthening treatment.
- the amount of molten salt discarded can be reduced, the danger associated with transporting the molten salt to be discarded can be reduced, and the load on the environment can be reduced.
- the chemically strengthened glass obtained by the chemical strengthening treatment using the regenerated salt exhibits good surface compressive stress and strength. Is very useful.
- FIG. 1 is a flowchart showing an embodiment of a method for regenerating a molten salt for glass chemical strengthening according to the present invention.
- FIG. 2 is a solubility curve showing measured values of the solubility of a salt that can be contained in the molten salt after glass chemical strengthening treatment with respect to 100 g of water.
- FIG. 3 is a graph showing the relationship between the number of recycles of regenerated salt obtained in Example 2 and the recovered salt recovery rate.
- FIG. 4 is a graph showing the relationship between the number of recycles of the regenerated salt obtained in Example 2 and the regenerated salt Na concentration.
- FIG. 5 is a graph showing the relationship between the number of recycles of regenerated salt obtained in Example 3 and the recovered salt recovery rate.
- FIG. 6 is a graph showing the relationship between the number of recycles of regenerated salt obtained in Example 3 and the regenerated salt Na concentration.
- FIG. 7 is a graph showing the relationship between the number of recycles of regenerated salt obtained in Example 4 and the recovered salt recovery rate.
- FIG. 8 is a graph showing the relationship between the number of recycles of regenerated salt obtained in Example 4 and the concentration of regenerated salt Na.
- the present invention is a method for regenerating a molten salt for chemical strengthening, the step of dissolving the molten salt after glass chemical strengthening treatment in water at a temperature below the melting point of the molten salt, cooling the obtained aqueous solution to obtain the regenerated salt. And a step of obtaining a moisture content in the regenerated salt of less than 5% by mass by drying.
- FIG. 1 shows an embodiment of a method for regenerating a molten salt for glass chemical strengthening according to the present invention.
- the chemical strengthening treatment of glass involves immersing glass as a raw material in a molten salt for glass strengthening (sometimes simply referred to as “molten salt”), and Na in the glass ion exchanges with K in the molten salt.
- molten salt for glass strengthening
- Na in the glass ion exchanges with K in the molten salt a compressive stress layer that is a high-density layer is formed on the glass surface.
- the molten salt in the present invention contains an inorganic potassium salt.
- the inorganic potassium salt preferably has a melting point below the strain point (usually 500 to 600 ° C.) of the glass to be chemically strengthened.
- a molten salt containing potassium nitrate (melting point 330 ° C.) as a main component (potassium nitrate molten) Salt) is preferred. If potassium nitrate is a main component, it is preferable because it is in a molten state below the strain point of glass and is easy to handle in the operating temperature range.
- the main component means that the content in the molten salt is 50% by mass or more.
- the molten salt is further selected from the group consisting of K 2 CO 3 , Na 2 CO 3 , KHCO 3 , NaHCO 3 , K 3 PO 4 , Na 3 PO 4 , K 2 SO 4 , Na 2 SO 4 , KOH and NaOH. It is preferable to contain at least one salt, and it is more preferable to contain at least one salt selected from the group consisting of K 2 CO 3 , Na 2 CO 3 , KHCO 3 and NaHCO 3 .
- the content of K 2 CO 3 in the molten salt is 0.1% by mass or more, and chemical strengthening is performed.
- the chemical strengthening treatment time is preferably 1 minute to 10 hours, more preferably 5 minutes to 8 hours, and even more preferably 10 minutes to 4 hours.
- the molten salt used for the chemical strengthening treatment in the present invention may contain other chemical species as long as the effects of the present invention are not impaired, for example, sodium chloride, potassium chloride, sodium borate, boric acid.
- alkali chlorides such as potassium and alkali borates. These may be added alone or in combination of two or more.
- the molten salt used for the glass chemical strengthening treatment can be produced by a known method, and the glass can be chemically strengthened by a known method using the molten salt.
- the molten salt is solidified by cooling or cooling the molten salt (waste salt) in which a desired surface compressive stress cannot be obtained by chemical strengthening treatment to a temperature below the melting point of the molten salt.
- the waste salt includes potassium nitrate and sodium nitrate.
- the waste salt includes potassium salt and sodium salt of the added salt. That is, for example, when potassium carbonate (K 2 CO 3 ) is added, the waste salt includes potassium carbonate and sodium carbonate.
- the concentration of Na in the waste salt is generally 4000 to 20000 mass ppm.
- the waste salt Na is present at a higher concentration than in the molten salt before the chemical strengthening treatment.
- the solid waste salt having a high Na concentration is taken out and dissolved in water.
- the waste salt in the solid state is preferably divided as appropriate in order to facilitate dissolution, and is preferably divided into, for example, a size of 1000 cm 3 or less.
- Water for dissolving the waste salt is not particularly limited, and pure water, distilled water, or the like can be used. From the viewpoint of preventing an increase in impurities contained in the aqueous solution, pure water having an electric conductivity of 10 ⁇ S or less is preferable. .
- the temperature of water at the time of dissolving the waste salt may be a temperature below the melting point of the molten salt, preferably 60 to 120 ° C, and more preferably 80 to 100 ° C from the viewpoint of easy handling. The water temperature can be appropriately adjusted by a known method such as a water bath or an oil bath.
- concentration of the waste salt in aqueous solution is so preferable that it is high, and it is more preferable to melt
- the stirring speed is usually 50 to 2000 rpm, preferably 100 to 1000 rpm.
- the waste salt When the waste salt is completely dissolved in the water, cool the aqueous solution.
- the desired salt contained in the waste salt is dissolved to saturation solubility, depending on the type of salt and the proportion contained in the waste salt, other salts may not be completely dissolved and remain in the aqueous solution as a solid. .
- the foreign material contained in waste salt may remain.
- the filtrate is cooled after removing undissolved salt and foreign matters by filtration or the like.
- the filtration accuracy is preferably 100 ⁇ m or less, more preferably 0.2 ⁇ m or more and 100 ⁇ m or less.
- the cooling can be performed by a known method such as natural cooling (cooling), water cooling, or ice cooling. Cooling is preferably performed to 25 ° C. or lower, more preferably 20 ° C. or lower, and further preferably 10 ° C. or lower, more preferably from the viewpoint of increasing the yield.
- the waste salt and the precipitate include potassium nitrate and sodium nitrate. Further, depending on the type of salt added to the molten salt, the precipitate contains the potassium salt or sodium salt of the added salt.
- FIG. 2 is a solubility curve (g / 100 g of water) of measured values showing the temperature dependence of solubility in water for potassium nitrate, sodium nitrate, potassium carbonate and sodium carbonate. According to this, when the temperature of the aqueous solution is around 70 ° C., the solubility of potassium nitrate is higher than that of sodium nitrate and potassium carbonate in the high temperature region, and the solubility of potassium nitrate is lower than that of sodium nitrate and potassium carbonate in the low temperature region.
- the difference between the saturation solubility at the dissolved temperature and the saturation solubility at the cooled temperature Of the salt precipitates as a solid.
- the salt to be used as the regenerated salt is potassium nitrate
- the difference in saturation solubility of potassium nitrate is larger than the difference in saturation solubility of other salts
- the precipitate deposited by cooling the aqueous solution is not discarded. It contains potassium nitrate at a higher rate than the salt, and the Na concentration in the precipitate is lower than the original waste salt. Therefore, the precipitate can be used again as a molten salt for glass chemical strengthening treatment, and can be called “regenerated salt”.
- recrystallization causes a salt with a low Na concentration from a waste salt with a high Na concentration. Can be played. If the Na concentration in the regenerated salt is 1000 mass ppm or less, it can be reused for the chemical strengthening treatment of glass.
- Concentration means to increase the salt concentration in the aqueous solution, but a known method such as vacuum concentration (vacuum concentration) or freeze concentration can be used. By concentrating the aqueous solution, a salt that can no longer be dissolved is deposited. By performing a combination of the cooling step and the concentration step of the aqueous solution, a regenerated salt having a lower Na concentration can be obtained with high efficiency.
- the obtained regenerated salt is precipitated in the aqueous solution
- solid-liquid separation is performed in order to use it again for the chemical strengthening treatment of glass.
- known methods such as filtration and centrifugation can be used.
- the molten salt for example, potassium nitrate
- the Na concentration in the liquid smoke increases, and accordingly, the Na concentration in the regenerated salt also increases. Therefore, it is preferable to discard a part of the liquid smoke and control the Na concentration.
- the amount of the liquid smoke to be reused can be determined in consideration of the Na concentration.
- the regenerated salt may be washed.
- the washing can be performed with pure water having an electric conductivity of 10 ⁇ S or less.
- the temperature of the washing water is preferably 20 ° C. or less.
- the yield of the regenerated salt obtained when washing is reduced, it is necessary to appropriately determine whether or not washing is necessary in consideration of the balance between the yield and purity according to the purpose.
- the washing liquid is further solid-liquid separated to obtain regenerated salt. Since the molten salt (for example, potassium nitrate) remains in the liquid after solid-liquid separation, a part of the liquid can be mixed and reused in the waste salt solution. However, when recycling is repeated by reusing the liquid smoke, the Na concentration in the liquid smoke increases, and accordingly, the Na concentration in the regenerated salt also increases. Therefore, it is preferable to discard a part of the liquid smoke and control the Na concentration. The amount of the liquid smoke to be reused can be determined in consideration of the Na concentration.
- the molten salt for example, potassium nitrate
- the regenerated salt before drying contains about 6% by mass of water.
- a stainless steel (SUS) container is used when the regenerated salt is heated to be subjected to chemical strengthening treatment to form a molten salt. If the amount of water in the regenerated salt is large, the regenerated salt is heated to form a molten salt. In the process, the SUS container corrodes. Due to the corrosion, suspended matters are generated in the molten salt, and if the glass is subjected to chemical strengthening treatment as it is, the performance of the resulting chemically strengthened glass is affected.
- the smaller the amount of water in the regenerated salt the better, preferably less than 5% by mass, more preferably less than 2% by mass, still more preferably less than 1% by mass, and particularly preferably less than 0.2% by mass.
- the water content in the regenerated salt can be measured by TGA (thermogravimetry). Distilled water produced by drying can be reused as a solvent for dissolving the waste salt. By reusing distilled water, it can contribute to the reduction of environmental burden.
- the drying temperature may usually be 40 to 300 ° C, more preferably 80 to 200 ° C.
- the drying time may usually be 1 to 12 hours, and more preferably 1 to 4 hours. Moreover, you may reduce pressure simultaneously with a heating at the time of drying.
- a known method such as a hot plate or heating vacuum drying can be used. It is preferable to store the regenerated salt after drying in a sealed container in order to prevent moisture from entering.
- the regenerated salt that has undergone the drying step can be used as a molten salt for glass chemical strengthening treatment by heating to a temperature at which the glass is chemically strengthened.
- the regenerated salt obtained by the present invention can be reused as a molten salt repeatedly by the regenerating treatment of the present invention after being used as a molten salt for glass chemical strengthening treatment.
- the regeneration method of the present invention by reusing a part of the liquid smoke after solid-liquid separation to dissolve the waste salt, the yield of the regenerated salt is increased while keeping the Na concentration in the regenerated salt below a predetermined level. Can be raised. If the filtrate is not reused, it is difficult to increase the yield of regenerated salt. On the other hand, when all the filtrates are reused, the Na concentration in the aqueous solution increases, and the Na concentration in the resulting regenerated salt also increases.
- the regenerated salt obtained by the present invention contains nitrous acid in the range of 10 to 100 ppm by weight.
- the amount of nitrous acid contained in a new potassium nitrate molten salt not subjected to chemical strengthening is usually 10 ppm by weight or less. It is thought that the nitric acid content increases because nitric acid in the molten salt changes to nitrous acid by repeated chemical strengthening.
- the nitrous acid content in the molten salt can be measured by a naphthylethylenediamine colorimetric method.
- the glass used for the chemical strengthening process in this invention should contain sodium and it has a composition which can be strengthened by shaping
- Specific examples include aluminosilicate glass, soda lime glass, borosilicate glass, lead glass, alkali barium glass, and aluminoborosilicate glass.
- aluminosilicate glass has a large amount of Na substitution in the glass, so that the molten salt is severely deteriorated. For this reason, it is preferable because the effect of the method for regenerating a molten salt according to the present invention can be remarkably obtained.
- the glass can be manufactured and formed based on known methods.
- the thickness of the glass used for the chemical strengthening treatment and the presence or absence of polishing are also arbitrary.
- ⁇ Evaluation method> (Measurement of Na concentration)
- the Na concentration in the waste salt and the regenerated salt was identified using an atomic absorption photometer “ZA-3300” manufactured by Hitachi High-Technologies Corporation.
- the surface compressive stress of the aluminosilicate glass after the chemical strengthening treatment was evaluated using a surface stress meter “FSM-6000LE” manufactured by Orihara Seisakusho.
- the amount of water contained in the regenerated salt was quantified using a heat drying moisture meter “MS-70” manufactured by A & D.
- the aluminosilicate glass was chemically strengthened in a molten salt consisting only of potassium nitrate.
- the chemical strengthening treatment temperature was 450 ° C.
- the Na concentration in the molten salt (waste salt) after the chemical strengthening treatment was 6000 ppm.
- the molten salt after the chemical strengthening treatment was naturally cooled to 25 ° C. to obtain a waste salt. 1000 g of solid waste salt was divided into sizes of 30 cm 3 or less, weighed into a 2000 mL beaker, and 800 g of pure water was added. While this was automatically stirred at 200 rpm, it was heated to 80 ° C. with a water bath to obtain an aqueous solution in which all waste salts were dissolved in pure water.
- the waste salt After confirming that the waste salt was completely dissolved, it was ice-cooled to 1 ° C. with automatic stirring at 200 to 300 rpm to precipitate (recrystallize) the salt.
- suction filtration was performed to separate the obtained salt crystals from the aqueous solution.
- the crystals separated by filtration were collected and dried on a hot plate set at 80 ° C. for 5 hours to obtain 903 g of regenerated salt.
- the obtained regenerated salt had a water content of 3% by mass and a nitrous acid content of 20 ppm.
- the recovery rate was actually 90% against the theoretical yield of 94% obtained from the solubility curve.
- the Na concentration in the obtained regenerated salt was 400 mass ppm.
- Example 1 The regenerated salt obtained in Example 1 was heated to 450 ° C. in a SUS container to form a molten salt, and aluminosilicate glass preheated to 200 to 400 ° C. was immersed therein for 2 hours for chemical strengthening treatment. At this time, no suspended matter due to SUS corrosion was visually confirmed in the molten salt.
- the glass was washed twice with ion exchange water at 20 to 80 ° C., and washed with running water with ion exchange water at room temperature.
- the initial surface compressive stress (initial CS) of the obtained chemically strengthened glass was 844 MPa.
- the initial CS when the aluminosilicate glass is chemically strengthened with new potassium nitrate not subjected to ion exchange treatment as a molten salt is 750 to 900 MPa.
- Example 2 150 kg of waste salt containing potassium nitrate as a main component and Na concentration of 10,000 ppm was put in a SUS container, and 90.3 kg of pure water was added. This was heated to 90 ° C. with an electric heater and dissolved with stirring. After completely dissolving, it was taken out into another SUS container, cooled to room temperature by allowing to cool, and the salt was precipitated. Next, centrifugation was carried out to separate the obtained salt crystals and the aqueous solution, and a salt and a filtrate having a water content of 2% by mass were obtained. The obtained salt was washed with pure water and centrifuged again to obtain a salt and a filtrate having a water content of 2% by mass.
- the obtained salt was dried at 200 ° C. for 8 hours to obtain a regenerated salt having a water content of 0.05 mass%, an Na concentration of 70 ppm, and a nitrous acid concentration of 40 ppm. Further, 43.7 kg of the filtrate obtained by centrifugation was discarded, and the remaining 104.8 kg of filtrate was placed in a SUS container together with 112.5 kg of waste salt, and 6.5 kg of pure water was added. This was similarly heated to 90 ° C. and dissolved with stirring. Thereafter, cooling, centrifugation, washing and centrifugation were performed to obtain a regenerated salt and a filtrate. Table 1 shows the experimental results obtained by repeating this. Table 2 shows the result of the simulation performed under the same conditions. Further, the graphs of these results are shown in FIGS.
- Example 2 The regenerated salt obtained in Example 2 was heated to 450 ° C. in a SUS container to form a molten salt, and the initial CS of the chemically strengthened glass obtained by performing chemical strengthening treatment in the same manner as in Example 1 was 786 MPa. .
- Example 3 In the simulation of Example 2, Table 3 shows the simulation result when the amount of discarded liquid is 53.7 kg, and Table 4 shows the simulation result when the amount of discarded waste is 33.7 kg. Moreover, what made these results into a graph is shown in FIG. 5 and FIG.
- Example 4 In the simulation of Example 2, the simulation results when all of the liquid smoke is discarded are shown in Table 5. Table 6 shows the simulation results when all of the liquid smoke is reused. Moreover, what made these results into a graph is shown in FIG. 7 and FIG.
- the regenerated salt obtained by the regenerating method according to the present invention has a very low water content and Na concentration, and even when reused as a molten salt for glass chemical strengthening treatment, It was found that a surface compressive stress equivalent to that of a new molten salt not subjected to ion exchange treatment can be applied. Further, the solubility curve shown in FIG. 2 suggests that the yield of the regenerated salt can be increased by lowering the precipitation temperature during recrystallization. Furthermore, it was found that the yield of regenerated salt can be increased by reusing the filtrate obtained during the solid-liquid separation. It was also found that the Na concentration in the regenerated salt obtained can be controlled by adjusting the amount of the liquid recycle to be reused.
- a regenerated salt having a performance equivalent to that of a new molten salt can be obtained by subjecting the used molten salt provided to the chemically strengthened glass to a regeneration treatment.
- This regeneration process can reduce the amount of used molten salt (waste salt) to be discarded, and can reduce the environmental impact and produce chemically tempered glass at a low cost, realizing high productivity. .
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Abstract
Description
化学強化の特性のひとつである表面圧縮応力(CS)は、硝酸カリウム溶融塩中のNa濃度増加に伴い低下するため、得られる化学強化ガラスのCS値が基準値を下回ると、当該溶融塩を廃棄し、新たな溶融塩を使用する必要がある。 When producing chemically strengthened glass by ion exchange of Na ions in glass and K ions in molten salt in molten salt containing potassium nitrate (potassium nitrate molten salt), it is melted from the glass as the chemical strengthening treatment is performed. The amount of Na dissolved in the salt increases, and the Na ion concentration in the molten salt increases.
Since the surface compressive stress (CS), which is one of the characteristics of chemical strengthening, decreases as the Na concentration in the potassium nitrate molten salt increases, the molten salt is discarded when the CS value of the resulting chemically strengthened glass falls below the reference value. However, it is necessary to use a new molten salt.
そこで特許文献1には、ガラス成分中のLi又はCsが不純物として溶融塩中に混入することが、当該溶融塩のイオン交換能力が低下する原因であるとして、高温溶融状態の塩を槽内の水中にシャワー状に降らせ、当該水中に溶融塩を溶解、冷却及び分離することにより、溶融塩を再生処理する方法が開示されている。 The molten salt in which the desired CS value cannot be obtained by the chemical strengthening treatment is usually allowed to cool and solidify, and then ground into small blocks and discarded. However, in the said processing method, waste molten salt (waste salt) cannot be used again, but there existed problems, such as having to use a large amount of molten salt.
Therefore, in Patent Document 1, it is assumed that Li or Cs in the glass component is mixed as an impurity in the molten salt, and that the ion exchange capacity of the molten salt is reduced. A method of regenerating a molten salt by allowing it to fall into water as a shower and dissolving, cooling and separating the molten salt in the water is disclosed.
そこで本発明では、ガラス性能への影響が少ないガラス化学強化処理用溶融塩の再生方法を提供することを目的とする。 However, in the process of heating the regenerated molten salt to a molten state again, the stainless steel container holding the molten salt may corrode. Due to this corrosion, floating substances are generated in the molten salt, and if the glass is chemically strengthened as it is, there is a concern that the performance of the resulting chemically strengthened glass will be affected.
Therefore, an object of the present invention is to provide a method for regenerating a molten salt for glass chemical strengthening treatment that has little influence on glass performance.
<1>ガラス化学強化用溶融塩の再生方法であって、ガラス化学強化処理後の溶融塩を前記溶融塩の融点未満の温度で水に溶解する工程、前記溶解工程で得られた水溶液を冷却して再生塩を得る工程、及び、乾燥により前記再生塩中の水分量を5質量%未満とする工程を含む、ガラス化学強化用溶融塩の再生方法。
<2>前記水溶液を冷却して再生塩を得る工程において、さらに前記水溶液を濃縮する工程を含む、前記<1>に記載のガラス化学強化用溶融塩の再生方法。
<3>前記ガラス化学強化用溶融塩が硝酸カリウムを含む、前記<1>又は<2>に記載のガラス化学強化用溶融塩の再生方法。
<4>前記乾燥工程において前記再生塩中の水分量を0.2質量%未満とする、前記<1>~<3>のいずれかに記載のガラス化学強化用溶融塩の再生方法。
<5>前記水溶液を冷却して再生塩を得る工程において、冷却した溶液を再生塩と濾液とに固液分離して、濾液の一部を前記溶解工程における溶解液に混合する、前記<1>~<4>のいずれかに記載のガラス化学強化用溶融塩の再生方法。
<6>前記固液分離により得られた再生塩を洗浄し、さらに再生塩と濾液とに固液分離して、濾液の一部を前記溶解工程における溶解液に混合する、前記<5>に記載のガラス化学強化用溶融塩の再生方法。 That is, the present invention relates to the following <1> to <6>.
<1> A method for regenerating a molten salt for glass chemical strengthening, the step of dissolving the molten salt after glass chemical strengthening treatment in water at a temperature lower than the melting point of the molten salt, and cooling the aqueous solution obtained in the melting step A method for regenerating a molten salt for strengthening glass chemistry, comprising a step of obtaining a regenerated salt and a step of drying to reduce the water content in the regenerated salt to less than 5% by mass.
<2> The method for regenerating a molten salt for strengthening glass chemistry according to <1>, wherein the step of cooling the aqueous solution to obtain a regenerated salt further includes a step of concentrating the aqueous solution.
<3> The method for regenerating a molten salt for glass chemical strengthening according to <1> or <2>, wherein the molten salt for glass chemical strengthening includes potassium nitrate.
<4> The method for regenerating a molten salt for glass chemical strengthening according to any one of <1> to <3>, wherein a moisture content in the regenerated salt is less than 0.2% by mass in the drying step.
<5> In the step of cooling the aqueous solution to obtain a regenerated salt, the cooled solution is solid-liquid separated into a regenerated salt and a filtrate, and a part of the filtrate is mixed with the solution in the dissolution step, <1 The method for regenerating a molten salt for glass chemical strengthening according to any one of> to <4>.
<6> The regenerated salt obtained by the solid-liquid separation is washed, further solid-liquid separated into a regenerated salt and a filtrate, and a part of the filtrate is mixed with the dissolved solution in the dissolving step. A method for regenerating a molten salt for glass chemical strengthening as described.
本明細書において“質量%”と“重量%”、“質量ppm”と“重量ppm”とは、それぞれ同義である。また、単に“ppm”と記載した場合は、“重量ppm”のことを示す。
また、本明細書において、「Na濃度」と表記した際は、Naとしての濃度を意味するものである。 Hereinafter, the present invention will be described in detail, but the present invention is not limited to the following embodiments, and can be arbitrarily modified without departing from the gist of the present invention.
In the present specification, “mass%” and “weight%”, “mass ppm” and “weight ppm” have the same meaning. In addition, when “ppm” is simply described, it indicates “weight ppm”.
In this specification, “Na concentration” means a concentration as Na.
本発明は化学強化用溶融塩の再生方法であって、ガラス化学強化処理後の溶融塩を前記溶融塩の融点未満の温度で水に溶解する工程、得られた水溶液を冷却して再生塩を得る工程、及び、乾燥により前記再生塩中の水分量を5質量%未満とする工程を含むことを特徴とする。 <Regeneration of molten salt>
The present invention is a method for regenerating a molten salt for chemical strengthening, the step of dissolving the molten salt after glass chemical strengthening treatment in water at a temperature below the melting point of the molten salt, cooling the obtained aqueous solution to obtain the regenerated salt. And a step of obtaining a moisture content in the regenerated salt of less than 5% by mass by drying.
廃塩中のNa濃度は一般的に4000~20000質量ppmである。 The molten salt is solidified by cooling or cooling the molten salt (waste salt) in which a desired surface compressive stress cannot be obtained by chemical strengthening treatment to a temperature below the melting point of the molten salt. When a molten salt containing potassium nitrate is used as the molten salt, the waste salt includes potassium nitrate and sodium nitrate. In addition, depending on the type of salt added to the molten salt, the waste salt includes potassium salt and sodium salt of the added salt. That is, for example, when potassium carbonate (K 2 CO 3 ) is added, the waste salt includes potassium carbonate and sodium carbonate.
The concentration of Na in the waste salt is generally 4000 to 20000 mass ppm.
廃塩溶解時の水の温度は溶融塩の融点未満の温度であればよく、60~120℃が好ましく、取り扱いの容易性から80~100℃がより好ましい。水温は、ウォーターバス、オイルバス等、公知の方法で適宜調整することができる。
なお、水溶液中の廃塩の濃度は高いほど好ましく、飽和溶解度まで溶解していることがより好ましい。また、廃塩全体の飽和溶解度ではなく、廃塩に含まれる複数の塩のうち、再生塩として利用したい所望の塩の飽和溶解度まで溶解させることも好ましい。 Water for dissolving the waste salt is not particularly limited, and pure water, distilled water, or the like can be used. From the viewpoint of preventing an increase in impurities contained in the aqueous solution, pure water having an electric conductivity of 10 μS or less is preferable. .
The temperature of water at the time of dissolving the waste salt may be a temperature below the melting point of the molten salt, preferably 60 to 120 ° C, and more preferably 80 to 100 ° C from the viewpoint of easy handling. The water temperature can be appropriately adjusted by a known method such as a water bath or an oil bath.
In addition, the density | concentration of the waste salt in aqueous solution is so preferable that it is high, and it is more preferable to melt | dissolve to saturation solubility. Moreover, it is also preferable to make it melt | dissolve not to the saturation solubility of the whole waste salt but to the saturation solubility of the desired salt to utilize as a regenerated salt among the plurality of salts contained in the waste salt.
これによれば、水溶液の温度が70℃付近を境に、高温領域では硝酸カリウムの溶解度が硝酸ナトリウム及び炭酸カリウムよりも高くなり、低温領域では硝酸カリウムの溶解度は硝酸ナトリウム及び炭酸カリウムよりも低くなる。
すなわち、硝酸カリウム、硝酸ナトリウム、炭酸カリウム及び炭酸ナトリウムの4種類の塩を含む廃塩を飽和溶解度まで溶解させた水溶液の場合、溶解させた温度における飽和溶解度と、冷却させた温度における飽和溶解度の差分の塩が固体として析出する。再生塩として使用したい塩を硝酸カリウムとした場合、硝酸カリウムの当該飽和溶解度の差が、その他の塩の飽和溶解度の差よりも大きい場合、該水溶液を冷却して析出した析出物は、もとの廃塩に比べて硝酸カリウムを高い割合で含んでおり、当該析出物中のNa濃度は、もとの廃塩よりも低くなる。そのため、当該析出物は、ガラス化学強化処理の溶融塩に再度使用することができ、「再生塩」と呼ぶことができる。 FIG. 2 is a solubility curve (g / 100 g of water) of measured values showing the temperature dependence of solubility in water for potassium nitrate, sodium nitrate, potassium carbonate and sodium carbonate.
According to this, when the temperature of the aqueous solution is around 70 ° C., the solubility of potassium nitrate is higher than that of sodium nitrate and potassium carbonate in the high temperature region, and the solubility of potassium nitrate is lower than that of sodium nitrate and potassium carbonate in the low temperature region.
That is, in the case of an aqueous solution in which waste salts containing four kinds of salts of potassium nitrate, sodium nitrate, potassium carbonate and sodium carbonate are dissolved to saturation solubility, the difference between the saturation solubility at the dissolved temperature and the saturation solubility at the cooled temperature Of the salt precipitates as a solid. When the salt to be used as the regenerated salt is potassium nitrate, when the difference in saturation solubility of potassium nitrate is larger than the difference in saturation solubility of other salts, the precipitate deposited by cooling the aqueous solution is not discarded. It contains potassium nitrate at a higher rate than the salt, and the Na concentration in the precipitate is lower than the original waste salt. Therefore, the precipitate can be used again as a molten salt for glass chemical strengthening treatment, and can be called “regenerated salt”.
濃縮とは水溶液中の塩濃度を高めることであるが、真空濃縮(減圧濃縮)や凍結濃縮等の公知の方法を用いることができる。水溶液を濃縮することにより、溶解しきれなくなった塩が析出する。水溶液の冷却工程と濃縮工程を組み合わせて行うことにより、より低Na濃度の再生塩を高効率に得ることができる。 It is also preferable to further concentrate the aqueous solution in the step of dissolving the waste salt in water and then cooling the obtained aqueous solution to obtain a regenerated salt.
Concentration means to increase the salt concentration in the aqueous solution, but a known method such as vacuum concentration (vacuum concentration) or freeze concentration can be used. By concentrating the aqueous solution, a salt that can no longer be dissolved is deposited. By performing a combination of the cooling step and the concentration step of the aqueous solution, a regenerated salt having a lower Na concentration can be obtained with high efficiency.
再生塩を化学強化処理に供するために加熱し溶融塩とする際に、ステンレス鋼(SUS)容器を使用するが、再生塩中の水分量が多いと、再生塩を加熱して溶融塩とする過程でSUS容器が腐食する。当該腐食により溶融塩中に浮遊物が発生し、そのままガラスの化学強化処理を行うと、得られる化学強化ガラスの性能に影響を及ぼす。そのため、再生塩中の水分量は少ないほど好ましく、好ましくは5質量%未満、より好ましくは2質量%未満、さらに好ましくは1質量%未満、特に好ましくは0.2質量%未満である。なお、再生塩中の水分量はTGA(熱重量測定法)によって測定することができる。乾燥によって生じる蒸留水は、廃塩を溶解する際の溶媒として再利用することができる。蒸留水を再利用することにより、環境負荷の低減に寄与することができる。 After recovering the regenerated salt by solid-liquid separation, it is preferable to dry well before reuse in the chemical strengthening treatment. By drying, the amount of water in the regenerated salt can be reduced. The regenerated salt before drying contains about 6% by mass of water.
A stainless steel (SUS) container is used when the regenerated salt is heated to be subjected to chemical strengthening treatment to form a molten salt. If the amount of water in the regenerated salt is large, the regenerated salt is heated to form a molten salt. In the process, the SUS container corrodes. Due to the corrosion, suspended matters are generated in the molten salt, and if the glass is subjected to chemical strengthening treatment as it is, the performance of the resulting chemically strengthened glass is affected. Therefore, the smaller the amount of water in the regenerated salt, the better, preferably less than 5% by mass, more preferably less than 2% by mass, still more preferably less than 1% by mass, and particularly preferably less than 0.2% by mass. The water content in the regenerated salt can be measured by TGA (thermogravimetry). Distilled water produced by drying can be reused as a solvent for dissolving the waste salt. By reusing distilled water, it can contribute to the reduction of environmental burden.
乾燥は、ホットプレートや加熱真空乾燥等の公知の方法を用いることができる。
乾燥後の再生塩は水分の混入を防ぐため、密閉容器に保存することが好ましい。 The drying temperature may usually be 40 to 300 ° C, more preferably 80 to 200 ° C. The drying time may usually be 1 to 12 hours, and more preferably 1 to 4 hours. Moreover, you may reduce pressure simultaneously with a heating at the time of drying.
For the drying, a known method such as a hot plate or heating vacuum drying can be used.
It is preferable to store the regenerated salt after drying in a sealed container in order to prevent moisture from entering.
中でも、アルミノシリケートガラスはガラス中のNa置換量が多いため溶融塩の劣化が激しい。このため、本発明に係る溶融塩の再生方法の効果を顕著に得ることができることから好ましい。 In addition, as long as the glass used for the chemical strengthening process in this invention should contain sodium and it has a composition which can be strengthened by shaping | molding and a chemical strengthening process, it is possible to use the thing of various compositions. it can. Specific examples include aluminosilicate glass, soda lime glass, borosilicate glass, lead glass, alkali barium glass, and aluminoborosilicate glass.
Among these, aluminosilicate glass has a large amount of Na substitution in the glass, so that the molten salt is severely deteriorated. For this reason, it is preferable because the effect of the method for regenerating a molten salt according to the present invention can be remarkably obtained.
<ガラス>
本実施例において、下記に示す組成(モル%)のアルミノシリケートガラスを用いた。SiO2 64.4%、Al2O3 8.0%、Na2O 12.5%、K2O 4.0%、MgO 10.5%、CaO 0.1%、SrO 0.1%、BaO 0.1%、ZrO2 2.5% EXAMPLES The present invention will be specifically described below with reference to examples, but the present invention is not limited to these.
<Glass>
In this example, an aluminosilicate glass having the following composition (mol%) was used. SiO 2 64.4%, Al 2 O 3 8.0%, Na 2 O 12.5%, K 2 O 4.0%, MgO 10.5%, CaO 0.1%, SrO 0.1%, BaO 0.1%, ZrO 2 2.5%
(Na濃度の測定)
本実施例において、廃塩及び再生塩中のNa濃度は、日立ハイテクノロジーズ社製の原子吸光光度計「ZA-3300」を使用して同定した。
(表面圧縮応力-CS-の測定)
化学強化処理後のアルミノシリケートガラスの表面圧縮応力は、折原製作所の表面応力計「FSM-6000LE」を使用して評価を行った。
(水分量の測定)
再生塩中に含まれる水分量は、エー・アンド・デー社製の加熱乾燥式水分計「MS-70」を使用して、定量を行った。 <Evaluation method>
(Measurement of Na concentration)
In this example, the Na concentration in the waste salt and the regenerated salt was identified using an atomic absorption photometer “ZA-3300” manufactured by Hitachi High-Technologies Corporation.
(Measurement of surface compressive stress -CS-)
The surface compressive stress of the aluminosilicate glass after the chemical strengthening treatment was evaluated using a surface stress meter “FSM-6000LE” manufactured by Orihara Seisakusho.
(Measurement of water content)
The amount of water contained in the regenerated salt was quantified using a heat drying moisture meter “MS-70” manufactured by A & D.
アルミノシリケートガラスを硝酸カリウムのみからなる溶融塩中で化学強化処理を行った。化学強化処理温度は450℃とした。化学強化処理後の溶融塩(廃塩)中のNa濃度は6000ppmであった。
化学強化処理後の溶融塩を25℃まで自然冷却し、廃塩を得た。
固体の廃塩1000gを30cm3以下のサイズに分割し、2000mLビーカーに秤量し、純水800gを加えた。これを200rpmで自動攪拌させながら、ウォーターバスで80℃に加温し、廃塩をすべて純水に溶解させた水溶液を得た。廃塩が完全に溶解したことを確認し、200~300rpmで自動攪拌しながら、1℃まで氷冷し、塩を析出(再結晶)させた。
次に、得られた塩の結晶と水溶液を分離するために吸引濾過を行った。濾別した結晶を回収し、80℃に設定したホットプレート上で5時間乾燥させることで、再生塩903gを得た。得られた再生塩中の水分量は3質量%、亜硝酸の含有量は20ppmであった。回収率は溶解度曲線から求めた理論収率94%に対し、実際には90%であった。また、得られた再生塩中のNa濃度は400質量ppmであった。 <Example 1>
The aluminosilicate glass was chemically strengthened in a molten salt consisting only of potassium nitrate. The chemical strengthening treatment temperature was 450 ° C. The Na concentration in the molten salt (waste salt) after the chemical strengthening treatment was 6000 ppm.
The molten salt after the chemical strengthening treatment was naturally cooled to 25 ° C. to obtain a waste salt.
1000 g of solid waste salt was divided into sizes of 30 cm 3 or less, weighed into a 2000 mL beaker, and 800 g of pure water was added. While this was automatically stirred at 200 rpm, it was heated to 80 ° C. with a water bath to obtain an aqueous solution in which all waste salts were dissolved in pure water. After confirming that the waste salt was completely dissolved, it was ice-cooled to 1 ° C. with automatic stirring at 200 to 300 rpm to precipitate (recrystallize) the salt.
Next, suction filtration was performed to separate the obtained salt crystals from the aqueous solution. The crystals separated by filtration were collected and dried on a hot plate set at 80 ° C. for 5 hours to obtain 903 g of regenerated salt. The obtained regenerated salt had a water content of 3% by mass and a nitrous acid content of 20 ppm. The recovery rate was actually 90% against the theoretical yield of 94% obtained from the solubility curve. Further, the Na concentration in the obtained regenerated salt was 400 mass ppm.
実施例1で得られた再生塩をSUS容器内で450℃まで加熱して溶融塩にし、そこに200~400℃に予熱したアルミノシリケートガラスを2時間浸漬することで化学強化処理を行った。このとき、溶融塩中にSUSの腐食による浮遊物は目視で確認されなかった。強化処理後、ガラスを20~80℃のイオン交換水で2回洗浄し、室温のイオン交換水で流水洗浄した。得られた化学強化ガラスの初期表面圧縮応力(初期CS)は844MPaであった。なお、イオン交換処理に供していない新品の硝酸カリウムを溶融塩として、アルミノシリケートガラスを化学強化処理した際の初期CSは750~900MPaである。 <Glass chemical strengthening treatment>
The regenerated salt obtained in Example 1 was heated to 450 ° C. in a SUS container to form a molten salt, and aluminosilicate glass preheated to 200 to 400 ° C. was immersed therein for 2 hours for chemical strengthening treatment. At this time, no suspended matter due to SUS corrosion was visually confirmed in the molten salt. After the tempering treatment, the glass was washed twice with ion exchange water at 20 to 80 ° C., and washed with running water with ion exchange water at room temperature. The initial surface compressive stress (initial CS) of the obtained chemically strengthened glass was 844 MPa. The initial CS when the aluminosilicate glass is chemically strengthened with new potassium nitrate not subjected to ion exchange treatment as a molten salt is 750 to 900 MPa.
硝酸カリウムを主成分とし、Na濃度が10,000ppmである廃塩150kgをSUS容器に入れ、純水90.3kgを加えた。これを電気ヒーターで90℃に加熱し、撹拌しながら溶解した。完全に溶解した後、別のSUS容器に取り出し、放冷により室温まで冷却し、塩を析出させた。次に、得られた塩の結晶と水溶液を分離するために遠心分離を行い、水分量が2質量%である塩と瀘液を得た。得られた塩を純水で洗浄し、再度遠心分離を行い、水分量が2質量%である塩と瀘液を得た。得られた塩を200℃で8時間乾燥し、水分量が0.05質量%、Na濃度が70ppm、亜硝酸濃度が40ppmの再生塩を得た。さらに、遠心分離で得た瀘液のうち43.7kgを廃棄し、残り104.8kgの瀘液を112.5kgの廃塩とともにSUS容器に入れ、純水6.5kgを追加した。これを同様に90℃に加熱し、撹拌しながら溶解した。その後、冷却、遠心分離、洗浄、遠心分離を行い、再生塩と瀘液を得た。これを繰り返し行った実験結果を表1に示す。また、同様の条件でシミュレーションを行った結果を表2に示す。さらに、これらの結果をグラフにしたものを図3および図4に示す。 <Example 2>
150 kg of waste salt containing potassium nitrate as a main component and Na concentration of 10,000 ppm was put in a SUS container, and 90.3 kg of pure water was added. This was heated to 90 ° C. with an electric heater and dissolved with stirring. After completely dissolving, it was taken out into another SUS container, cooled to room temperature by allowing to cool, and the salt was precipitated. Next, centrifugation was carried out to separate the obtained salt crystals and the aqueous solution, and a salt and a filtrate having a water content of 2% by mass were obtained. The obtained salt was washed with pure water and centrifuged again to obtain a salt and a filtrate having a water content of 2% by mass. The obtained salt was dried at 200 ° C. for 8 hours to obtain a regenerated salt having a water content of 0.05 mass%, an Na concentration of 70 ppm, and a nitrous acid concentration of 40 ppm. Further, 43.7 kg of the filtrate obtained by centrifugation was discarded, and the remaining 104.8 kg of filtrate was placed in a SUS container together with 112.5 kg of waste salt, and 6.5 kg of pure water was added. This was similarly heated to 90 ° C. and dissolved with stirring. Thereafter, cooling, centrifugation, washing and centrifugation were performed to obtain a regenerated salt and a filtrate. Table 1 shows the experimental results obtained by repeating this. Table 2 shows the result of the simulation performed under the same conditions. Further, the graphs of these results are shown in FIGS.
実施例2で得られた再生塩をSUS容器内で450℃まで加熱して溶融塩にし、実施例1と同様に化学強化処理を行って得られた化学強化ガラスの初期CSは786MPaであった。 <Chemical strengthening treatment>
The regenerated salt obtained in Example 2 was heated to 450 ° C. in a SUS container to form a molten salt, and the initial CS of the chemically strengthened glass obtained by performing chemical strengthening treatment in the same manner as in Example 1 was 786 MPa. .
実施例2のシミュレーションにおいて、瀘液の廃棄量を53.7kgとした場合のシミュレーション結果を表3に、瀘液の廃棄量を33.7kgとした場合のシミュレーション結果を表4に示す。また、これらの結果をグラフにしたものを図5および図6に示す。 <Example 3>
In the simulation of Example 2, Table 3 shows the simulation result when the amount of discarded liquid is 53.7 kg, and Table 4 shows the simulation result when the amount of discarded waste is 33.7 kg. Moreover, what made these results into a graph is shown in FIG. 5 and FIG.
実施例2のシミュレーションにおいて、瀘液の全てを廃棄した場合のシミュレーション結果を表5に示す。瀘液の全てを再利用した場合のシミュレーション結果を表6に示す。また、これらの結果をグラフにしたものを図7および図8に示す。 <Example 4>
In the simulation of Example 2, the simulation results when all of the liquid smoke is discarded are shown in Table 5. Table 6 shows the simulation results when all of the liquid smoke is reused. Moreover, what made these results into a graph is shown in FIG. 7 and FIG.
また、図2に示した溶解度曲線から、再生塩の収率は、再結晶時の析出温度を下げるとより高めることができる可能性が示唆された。
さらに、固液分離の際に得られる瀘液を再利用することにより、再生塩の収率を高めることができることが分かった。また、再利用する瀘液の量を調整することにより、得られる再生塩中のNa濃度をコントロールできることが分かった。 From the above results, the regenerated salt obtained by the regenerating method according to the present invention has a very low water content and Na concentration, and even when reused as a molten salt for glass chemical strengthening treatment, It was found that a surface compressive stress equivalent to that of a new molten salt not subjected to ion exchange treatment can be applied.
Further, the solubility curve shown in FIG. 2 suggests that the yield of the regenerated salt can be increased by lowering the precipitation temperature during recrystallization.
Furthermore, it was found that the yield of regenerated salt can be increased by reusing the filtrate obtained during the solid-liquid separation. It was also found that the Na concentration in the regenerated salt obtained can be controlled by adjusting the amount of the liquid recycle to be reused.
Claims (6)
- ガラス化学強化用溶融塩の再生方法であって、
ガラス化学強化処理後の溶融塩を前記溶融塩の融点未満の温度で水に溶解する工程、前記溶解工程で得られた水溶液を冷却して再生塩を得る工程、及び、乾燥により前記再生塩中の水分量を5質量%未満とする工程を含む、ガラス化学強化用溶融塩の再生方法。 A method for regenerating a molten salt for strengthening glass chemistry,
A step of dissolving the molten salt after glass chemical strengthening treatment in water at a temperature lower than the melting point of the molten salt, a step of cooling the aqueous solution obtained in the dissolving step to obtain a regenerated salt, and drying in the regenerated salt A method for regenerating a molten salt for strengthening glass chemistry, comprising a step of setting the moisture content of the glass to less than 5% by mass. - 前記水溶液を冷却して再生塩を得る工程において、さらに前記水溶液を濃縮する工程を含む、請求項1に記載のガラス化学強化用溶融塩の再生方法。 The method for regenerating a molten salt for glass chemical strengthening according to claim 1, wherein the step of cooling the aqueous solution to obtain a regenerated salt further comprises a step of concentrating the aqueous solution.
- 前記ガラス化学強化用溶融塩が硝酸カリウムを含む、請求項1又は2に記載のガラス化学強化用溶融塩の再生方法。 The method for regenerating a molten salt for glass chemical strengthening according to claim 1 or 2, wherein the molten salt for glass chemical strengthening contains potassium nitrate.
- 前記乾燥工程において前記再生塩中の水分量を0.2質量%未満とする、請求項1~3のいずれか一項に記載のガラス化学強化用溶融塩の再生方法。 The method for regenerating a molten salt for glass chemical strengthening according to any one of claims 1 to 3, wherein the moisture content in the regenerated salt is less than 0.2% by mass in the drying step.
- 前記水溶液を冷却して再生塩を得る工程において、冷却した溶液を再生塩と濾液とに固液分離して、濾液の一部を前記溶解工程における溶解液に混合する、請求項1~4のいずれか一項に記載のガラス化学強化用溶融塩の再生方法。 In the step of cooling the aqueous solution to obtain a regenerated salt, the cooled solution is subjected to solid-liquid separation into a regenerated salt and a filtrate, and a part of the filtrate is mixed with the solution in the dissolution step. The regeneration method of the molten salt for glass chemical strengthening as described in any one of Claims.
- 前記固液分離により得られた再生塩を洗浄し、さらに再生塩と濾液とに固液分離して、濾液の一部を前記溶解工程における溶解液に混合する、請求項5に記載のガラス化学強化用溶融塩の再生方法。
The glass chemistry according to claim 5, wherein the regenerated salt obtained by the solid-liquid separation is washed, further solid-liquid separated into a regenerated salt and a filtrate, and a part of the filtrate is mixed with the dissolved solution in the dissolving step. A method for recycling molten salt for strengthening.
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PCT/JP2014/081085 WO2015080095A1 (en) | 2013-11-29 | 2014-11-25 | Method for regenerating molten salt for chemical reinforcement of glass |
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JP (1) | JP6455441B2 (en) |
CN (1) | CN105555730B (en) |
TW (1) | TW201527236A (en) |
WO (1) | WO2015080095A1 (en) |
Cited By (7)
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WO2018155456A1 (en) * | 2017-02-24 | 2018-08-30 | Agc株式会社 | Chemically tempered glass plate and production method therefor |
US10351472B2 (en) | 2016-08-10 | 2019-07-16 | Corning Incorporated | Methods for reducing surface defects |
US10556826B2 (en) | 2015-11-20 | 2020-02-11 | Corning Incorporated | Methods for regenerating lithium-enriched salt baths |
US20210107827A1 (en) * | 2018-06-21 | 2021-04-15 | Schott Glass Technologies (Suzhou) Co. Ltd. | Chemically toughened glass article having no optical orange skin and method for producing same |
WO2022005958A1 (en) * | 2020-06-30 | 2022-01-06 | Corning Incorporated | Methods of regenerating poisoned molten salt baths with glass and associated glass compositions |
WO2022039932A1 (en) * | 2020-08-17 | 2022-02-24 | Corning Incorporated | Systems and methods for recycling waste ion exchange materials |
US11648549B2 (en) | 2018-11-29 | 2023-05-16 | Corning Incorporated | Ion exchange systems and methods for ion exchanging glass articles |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN107311205B (en) * | 2017-08-15 | 2018-11-27 | 东旭科技集团有限公司 | The method for purifying potassium nitrate in tempered glass waste liquid |
CN110711764A (en) * | 2019-10-29 | 2020-01-21 | 江苏盛勤环境工程有限公司 | Solid waste salt recycling process technology |
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JPS61291037A (en) * | 1985-06-17 | 1986-12-20 | Nippon Sheet Glass Co Ltd | Method for purifying molten salt |
JP2013067555A (en) * | 2011-09-09 | 2013-04-18 | Hoya Corp | Method for producing cover glass for potable appliance |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
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JP6024881B2 (en) * | 2011-09-09 | 2016-11-16 | Hoya株式会社 | Ion exchange glass article manufacturing method |
CN103466664B (en) * | 2013-09-17 | 2015-07-08 | 蓝思科技股份有限公司 | Fully-automatic production line type potassium nitrate recovering process |
-
2014
- 2014-11-25 WO PCT/JP2014/081085 patent/WO2015080095A1/en active Application Filing
- 2014-11-25 JP JP2015550932A patent/JP6455441B2/en active Active
- 2014-11-25 CN CN201480051561.2A patent/CN105555730B/en active Active
- 2014-11-28 TW TW103141500A patent/TW201527236A/en unknown
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
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JPS61291037A (en) * | 1985-06-17 | 1986-12-20 | Nippon Sheet Glass Co Ltd | Method for purifying molten salt |
JP2013067555A (en) * | 2011-09-09 | 2013-04-18 | Hoya Corp | Method for producing cover glass for potable appliance |
Cited By (14)
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US11161781B2 (en) | 2015-11-20 | 2021-11-02 | Corning Incorporated | Methods for regenerating lithium-enriched salt baths |
US10556826B2 (en) | 2015-11-20 | 2020-02-11 | Corning Incorporated | Methods for regenerating lithium-enriched salt baths |
US10843963B2 (en) | 2015-11-20 | 2020-11-24 | Corning Incorporated | Methods for regenerating lithium-enriched salt baths |
US10351472B2 (en) | 2016-08-10 | 2019-07-16 | Corning Incorporated | Methods for reducing surface defects |
US11261129B2 (en) | 2016-08-10 | 2022-03-01 | Corning Incorporated | Methods for reducing surface defects |
WO2018155456A1 (en) * | 2017-02-24 | 2018-08-30 | Agc株式会社 | Chemically tempered glass plate and production method therefor |
JP7044101B2 (en) | 2017-02-24 | 2022-03-30 | Agc株式会社 | Chemically tempered glass plate and its manufacturing method |
JPWO2018155456A1 (en) * | 2017-02-24 | 2019-12-12 | Agc株式会社 | Chemically tempered glass plate and manufacturing method thereof |
US20210107827A1 (en) * | 2018-06-21 | 2021-04-15 | Schott Glass Technologies (Suzhou) Co. Ltd. | Chemically toughened glass article having no optical orange skin and method for producing same |
US11932570B2 (en) * | 2018-06-21 | 2024-03-19 | Schott Glass Technologies (Suzhou) Co. Ltd. | Chemically toughened glass article having no optical orange skin and method for producing same |
US11648549B2 (en) | 2018-11-29 | 2023-05-16 | Corning Incorporated | Ion exchange systems and methods for ion exchanging glass articles |
WO2022005958A1 (en) * | 2020-06-30 | 2022-01-06 | Corning Incorporated | Methods of regenerating poisoned molten salt baths with glass and associated glass compositions |
WO2022039932A1 (en) * | 2020-08-17 | 2022-02-24 | Corning Incorporated | Systems and methods for recycling waste ion exchange materials |
US11865532B2 (en) | 2020-08-17 | 2024-01-09 | Corning Incorporated | Systems and methods for recycling waste ion exchange materials |
Also Published As
Publication number | Publication date |
---|---|
JP6455441B2 (en) | 2019-01-23 |
CN105555730A (en) | 2016-05-04 |
JPWO2015080095A1 (en) | 2017-03-16 |
CN105555730B (en) | 2018-09-18 |
TW201527236A (en) | 2015-07-16 |
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