WO2007097124A1 - Treatment method for converting waste asbestos into harmless products, process for production of zeolite, and intermediates for the production - Google Patents
Treatment method for converting waste asbestos into harmless products, process for production of zeolite, and intermediates for the production Download PDFInfo
- Publication number
- WO2007097124A1 WO2007097124A1 PCT/JP2007/000116 JP2007000116W WO2007097124A1 WO 2007097124 A1 WO2007097124 A1 WO 2007097124A1 JP 2007000116 W JP2007000116 W JP 2007000116W WO 2007097124 A1 WO2007097124 A1 WO 2007097124A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- aluminum
- asbestos
- solid solution
- silicon
- waste
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B39/00—Compounds having molecular sieve and base-exchange properties, e.g. crystalline zeolites; Their preparation; After-treatment, e.g. ion-exchange or dealumination
- C01B39/02—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof; Direct preparation thereof; Preparation thereof starting from a reaction mixture containing a crystalline zeolite of another type, or from preformed reactants; After-treatment thereof
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
- B09B3/35—Shredding, crushing or cutting
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/70—Chemical treatment, e.g. pH adjustment or oxidation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B2101/00—Type of solid waste
- B09B2101/35—Asbestos
Definitions
- the present invention relates to a method for detoxifying waste asbestos, a method for producing zeoli cake using waste asbestos, and a silicon-containing solid solution and a key-aluminum-containing solid solution as intermediates for the production.
- Asbestos is a mineral fiber having a needle-like crystal structure, and when a person inhales the dust, it causes serious diseases such as malignant mesothelioma.
- the asbestos consumed in Japan from 1930 to 2000 was 10 million tons, and about 90% of imported Aspes was used for building materials. As demolition of buildings that use Aspest-containing building materials will peak, the problems of Aspest exposure and disposal will become serious and become a social problem.
- Patent Documents As a method for treating asbestos waste and calcium silicate waste, asbestos and calcium silicate or alumina are mixed and melted at a temperature around 1300 ° C to make them harmless (Patent Documents) 1) or as a method for treating waste asbestos materials, etc.
- waste asbestos and aluminum loss which is a by-product of aluminum smelting, are mixed and fired at 80 ° C or higher. There is known a method of reusing it as a raw material (see Patent Document 3).
- zeolite is a general term for aluminosilicates with fine pores in the crystal, and has a structure (S i-0-AI-0-si) in which silicon and aluminum are bonded via oxygen.
- the basic skeleton is formed by three-dimensional combination.
- Zeolite is generally manufactured by mixing and firing sodium silicate and sodium aluminate solutions.
- incineration ash, waste waste sand, coal ash A method for producing zeolite using combustible wastes such as the above has been studied (see, for example, Patent Documents 4 and 5), and has recently been put into practical use.
- Patent Document 1 Japanese Patent Application Laid-Open No. 4 _ 1 8 8 7 9
- Patent Document 2 JP-A-5-1 3 8 1 4 7
- Patent Document 3 Japanese Patent Laid-Open No. 6-1 3 4 4 3 8
- Patent Document 4 Japanese Patent Laid-Open No. 1 1-1 9 9 2 2 5
- Patent Document 5 Japanese Patent Laid-Open No. 2 00 0 _ 1 5 9 5 1 7
- an object of the present invention is to provide a method for producing zeolite using detoxified waste asbestos, and a production intermediate thereof.
- Another object of the present invention is to provide a method for producing zeolite candy that can be easily and safely reused at low cost, and a production intermediate thereof.
- Another object of the present invention is to provide a method for detoxifying harmful waste asbestos simply and at low cost.
- waste asbestos and aluminate or a salt thereof are mixed and then heat-treated at 70 to 100 ° C. to obtain a carbon-aluminum-containing solid solution.
- This is a detoxification method for waste asbestos.
- the present invention is characterized in that waste asbestos and a silicon-containing substance are mixed and then heat-treated at 70 ° C to 100 ° C to obtain a silicon-containing solid solution. This is a detoxification method for waste Aspes.
- the present invention is characterized in that asbestos and an aluminum-containing substance are mixed and then heat-treated to form a carbon / aluminum-containing solid solution, and then the alkali / aluminum-containing solid solution is alkali-treated. This is a method for producing zeolite.
- the aluminum-containing substance may be aluminate or The method for producing a zeolite according to (3), characterized in that it is a salt of
- the present invention is the method for producing a zeolite according to (3), wherein the heat treatment is performed at 700 ° C or higher.
- the present invention is the method for producing a zeolite according to (3), wherein the heat treatment is performed at 700 to 1,000 ° C.
- the present invention is characterized in that the above-mentioned key substance-containing substance is a key acid or a salt thereof, and the above-mentioned aluminum-containing substance is an aluminate or a salt thereof.
- the present invention is the method for producing a zeolite according to (7), wherein the heat treatment is performed at 700 ° C or higher.
- the present invention provides the method for producing a zeolite according to (7), wherein the heat treatment is performed at 700 to 1,000 ° C.
- the present invention is characterized in that asbestos is heat-treated to form molten slag, and then the molten slag and the aluminum-containing material are mixed and then subjected to an al force treatment. It is a manufacturing method of a kite.
- the present invention is also characterized in that it is obtained by mixing asbestos and aluminate or a salt thereof, and then heat-treating at 700 to 1 000 ° C. It is a contained solid solution.
- the present invention is characterized in that it is obtained by mixing asbestos and aluminate or a salt thereof and then heat-treating at 800 to 900 ° C. It is a solid solution.
- the present invention provides the silicon-containing solid solution as described in (14) or (15), wherein the key substance is a key acid or a salt thereof.
- the raw material mixture containing waste asbestos can be melted and solidified at an extremely low temperature compared to the conventional method, and the needle-like crystal structure of the asbestos cake can be eliminated and rendered harmless.
- the needle-like crystal structure of the asbestos cake can be eliminated and rendered harmless.
- waste asbestos can be rendered harmless at an extremely low temperature as compared with the conventional method, and the product is in powder form, so that it is easy to handle.
- Zeolite can be manufactured using raw materials with excellent transportability.
- waste asbestos can be rendered harmless at an extremely low temperature as compared with the conventional method, and it becomes a source of harmful gas in the raw material mixture containing waste asbestos. Because it does not contain any substances that can be obtained, zeolite can be manufactured using highly safe raw materials.
- asbestos and an aluminum-containing substance are mixed and then heat-treated to form a carbon-aluminum-containing solid solution, and then the silicon-aluminum-containing solid solution is subjected to an aluminum force treatment.
- This is a method for producing zeoli rice cake.
- the asbestos used in the production of the zeorai rice cake of the present embodiment is particularly limited. Serinolite chrysotile (spar asbestos ⁇ Mg 6 S i 4 O 10 (OH) 8 ), amphibolite crosilite (Ao Asbestos, Na 2 (F e 2 + > M g ) 3 (F e 3+ ) 2 Si 8 0 22 (OH) 2 ), Amosite ((Mg ⁇ F e 2 + ) 7 Si 8 0 22 (OH) 2 ), Anthophyllite ((Mg> F e 2 + ) 7 S i 8 0 22 (OH) 2 ), tremolite (Ca 2 Mg 5 S i 8 0 22 (OH) 2 ), actinolite (Ca 2 (Mg, F e 2 +) 5 S i It is possible to detoxify waste containing various asbestos such as 8 0 22 (OH) 2 ).
- the aluminum-containing material used in the present embodiment is a material that can be used as a raw material for zeoli cake, and is not particularly limited as long as it does not generate hydrogen gas.
- Aluminates such as magnesium aluminate can be used alone or in combination of two or more. Of these, aluminate or a salt thereof is preferable, and sodium aluminate is preferably used in the present invention.
- waste asbestos and aluminium-containing material are mixed well.
- the mixing ratio of the waste asbestos and the aluminum-containing substance is in a range in which the molar ratio of silicon to aluminum in the raw material is 10: 1 to 1: 4, preferably 2: 1 to 1: 2.
- the raw material mixing method include a method of directly pulverizing and mixing the raw material using a mixer, a pulverizer, etc., a method of dissolving and suspending the raw material using a solvent such as water, and stirring and mixing. There is no particular limitation.
- the obtained mixture of waste asbestos and aluminum-containing material is heat-treated.
- the heat treatment method include a method using an electric furnace, a method using microwave irradiation, a method using a microwave, a high frequency, a low frequency, a microplasma, a high frequency plasma, and the like. Among these, shortening of processing time The method using an electric furnace is particularly preferable from the viewpoint of downsizing the apparatus.
- the temperature of the heat treatment is 100 ° C or higher, preferably in the range of 700 ° C to 1 000 ° C, and more preferably in the range of 800 ° C to 900 ° C. If the processing temperature is less than 700 ° C, the needle-like crystal structure of Aspes ⁇ remains and cannot be completely detoxified, and if it exceeds 1 000 ° C, detoxification is achieved and the processing temperature cannot be further increased. This is because the cost increases. Furthermore, since the formed silicon-aluminum-containing solid solution is hard and rocky, it needs to be pulverized, and the manufacturing process becomes complicated, which is not preferable. Here, the melting temperature of asbestos alone is about 1500 ° C.
- the raw material mixture containing waste asbestos is melted and dissolved at an extremely low temperature, and the needle-like crystal structure of Aspes Can be eliminated and rendered harmless, so the cost of the harmless treatment can be reduced.
- the treatment time is a time sufficient for the raw material mixture to melt and dissolve at the treatment temperature, and is appropriately determined depending on the treatment temperature and the amount of the raw material mixture.
- zeolite is generated by subjecting a key alloy-containing solid solution obtained by cooling and solidification after heat treatment to an Al force treatment.
- alkali used for the alkali treatment include sodium hydroxide, potassium hydroxide, calcium hydroxide and the like, but are not particularly limited thereto.
- Treatment conditions are as follows: At normal pressure, alkali concentration is 0.5 to 5 N, preferably 1.5 to 3.5 N, treatment temperature is 80 to 100 ° C, preferably 90 to 95 ° C, treatment time Is 0.5 to 48 hours, preferably 1 to 24 hours.
- the Al force treatment may be performed under a pressure of 1 to 5 atm, preferably 1.25 to 2 atm, in which case the alkali concentration is 0.5 to 51 ⁇ 1, preferably ⁇ 1. 5 to 3.5 N, treatment temperature is 120 to 230 ° C, preferably 130 to 150 ° C, and treatment time is 0.5 to 24 hours, preferably 1 to 10 hours. If these treatment conditions are less than the above lower limit, sufficient gelation cannot be obtained, and if the above upper limit is exceeded, excessive conditions will be caused, which may cause adverse effects such as damage to the container.
- the product obtained by the above-described Al force treatment is obtained by filtration or centrifugation. By drying, the desired zeolite can be obtained.
- the key-containing substance used in the present embodiment is not particularly limited as long as it is a key-containing substance.
- a sodium salt, a key salt such as sodium key acid examples thereof include silicate glass such as kainate glass, soda lime glass, potash lime glass, diatomaceous earth, kaolin, and metakaolin, and these can be used alone or in combination of two or more.
- silicate glass such as kainate glass, soda lime glass, potash lime glass, diatomaceous earth, kaolin, and metakaolin
- kaic acid or a salt thereof is preferable, and sodium kaate is preferably used in the present invention.
- the raw material waste asbestos, the aluminum-containing material, the raw material mixing method, the heat treatment method, the temperature, the time, etc. used in the present embodiment are the same as those in the first embodiment. is there.
- an aluminum-containing substance is mixed with the silicon-containing solid solution obtained by cooling and solidifying after the heat treatment, and the resulting mixture is subjected to al force retreatment to obtain a lysate. Generate.
- the mixing ratio of the silicon-containing solid solution and the aluminum-containing substance is such that the molar ratio of the silicon and the aluminum in the raw material is 10: 1 to 1: 4, preferably 2: 1 to 1: 2.
- the mixing method, alkali treatment method, conditions, and the like are the same as those in the first embodiment.
- the asbestos is produced by heat-treating asbestos into molten slag, then mixing the molten slag and the aluminum-containing substance, and then subjecting to asphalt treatment. Is the method.
- the asbestos and aluminum-containing material used in the present embodiment is
- asbestos is heat-treated at about 150 ° C to obtain molten slag.
- the heat treatment method and conditions are the same as those in the first embodiment. It is the same as the case where it can be placed.
- molten slag and an aluminum-containing material are mixed, and the resulting mixture is alkali-treated to obtain zeolite.
- the method of mixing the raw materials, the method and conditions of the power treatment, etc. are the same as those in the first embodiment.
- various zeolites such as sodalite, zeolite hA, zeolite p, and the like are adjusted by appropriately adjusting various conditions such as the ratio of silicon to aluminum in the raw material and the pressure of the alkali treatment. Can be manufactured.
- a fourth embodiment of the present invention is obtained by mixing asbestos and a silicon-containing substance and then heat-treating at 700 to 100 ° C. It is a solid solution.
- the method for producing the silicon-containing solid solution of the present embodiment is the same as that in the second embodiment.
- a fifth embodiment of the present invention is a silicon / aluminum-containing solid solution obtained by mixing asbestos and sodium aluminate, followed by heat treatment at 700 to 100 ° C.
- the method for producing the silicon-aluminum-containing solid solution of the present embodiment is the same as in the first embodiment.
- Non-oxidizing atmosphere quenching furnace (Thermal SAD 330 type), Operating temperature: 600-1060 ° C, Heating furnace effective dimension: 027 OXH 2 OO, Processing amount: 25 kg / gross (Jig ⁇ (Including tray) Oil tank: Approximately 250 liters, conducted under nitrogen flow
- FIGS. 1 and 2 An optical microscope (simple incident polarization) photograph and an electron microscope photograph of the waste asbestos used are shown in FIGS. 1 and 2, respectively.
- Figure 3 shows the results of the identification of matching peaks with the J CPDS card chart of the used asbestos powder X-ray diffraction.
- Example 2 Preparation of zeolite from solid solution containing aluminum ⁇ [0064] 5 g of the solid solution obtained in Example 1 was added to 3.5 N sodium hydroxide solution 100 m
- Fig. 5 shows an electron micrograph of the final product obtained
- Fig. 6 (b) shows the result of powder X-ray diffraction
- Fig. 7 shows the identification result based on the matching peak with the J CP DS card chart by powder X-ray diffraction
- Figure 8 (b) shows the external appearance and, respectively.
- Example 2 From Fig. 9, it was found that the zeolite obtained in Example 2 has the same excellent adsorbing ability as the waste waste-derived zeolite and the coal ash-derived zeolite.
- the heat treatment was carried out in the same manner as in Example 1 except that the heat treatment temperatures were set to 700 ° C, 800 ° C, and 900 ° C, respectively. 6 g was obtained.
- Fig. 10 (a), Fig. 11 (a) and Fig. 12 (a) show the appearance photographs of the obtained solid solutions, and Fig. 13 to Fig. 15 show the electron micrographs of the obtained solid solutions. Shown respectively. From Fig. 10 to Fig. 12 these solid solutions are obtained in powder form, and from Fig. 13 to Fig. 15 the waste asbestos becomes a solid solution even at a low temperature of 700 to 900 ° C, and the acicular crystal structure disappears. I was able to make it harmless. At a heat treatment temperature of 700 ° C, a slight asbestos needle-like crystal structure is observed, but it is thought that it is almost harmless.
- Example 2 The same treatment as in Example 2 was carried out except that 5.5 g of the solid solution obtained above was used to obtain final products of 3.8 g, 3.7 g, and 3.6 g, respectively. .
- the electron micrographs of the final product obtained are shown in Figs. 16 to 18, the results of powder X-ray diffraction are shown in Figs. 19 (a), (b), and (c), and the appearance photo is shown in Fig. 1. This is shown in Fig. 1 (b), Fig. 1 1 (b) and Fig. 1 2 (b), respectively.
- Example 2 The same procedures as in Example 2 were performed except that 10 g of the solid solution obtained above was used, respectively, to obtain final products of 4.57 g, 4.11 g, and 3.36 g, respectively.
- the Electron micrographs of the final product obtained are shown in FIGS. 25 to 27, respectively.
- the weight ratio of waste asbestos to sodium aluminate is 4: 1 to 10: 1 (the molar ratio of silicon to aluminum is 4: 1 to 10: 1).
- the weight ratio of waste asbestos to sodium aluminate 2: 1 to 1: 1 (the molar ratio of key to aluminum 2: 1 to 1: 1), the acicular crystal structure is It was found that it disappeared and became completely harmless.
- the final product is waste asbestos and aluminate.
- the sodium weight ratios of 1: 1 to 10: 1 the molar ratio of kaen to aluminum of 1: 1 to 10: 1
- the needle-like crystal structure of Aspes was not observed, and it was completely detoxified. I was able to generate.
- Example 8 Preparation of other types of zeolite from solid solution containing aluminum [0086] 29 g of sodium aluminate was dissolved in 2 OOm I of water to obtain a sodium aluminate solution. Further, 112 g of sodium hydroxide was dissolved in 268 g of water, and 420 g of sodium silicate was added to obtain a sodium silicate solution. The obtained sodium aluminate solution and sodium silicate solution were mixed and aged at 15 ° C. for 16 hours to form a slurry.
- Example 2 The same treatment as in Example 2 was carried out except that the solid solution obtained above was used to obtain 0.42 g of the final product.
- the electron micrograph of the final product obtained is shown in Fig. 39, and the results of powder X-ray diffraction are shown in Fig. 40 (a).
- the result of powder X-ray diffraction of the final product of Example 2 (heat treatment in a non-oxidizing atmosphere quenching furnace) is shown in FIG. 40 (b).
- FIG. 45 shows an electron micrograph of the final product obtained
- FIG. 46 (b) shows the result of powder X-ray diffraction.
- Example 12 The same treatment as in Example 12 was conducted except that 20 g of molten slag was used instead of molten slag and sodium aluminate. 1 04. 2 ⁇ 1 ⁇ 2) was obtained. An electron micrograph of the final product obtained is shown in FIG.
- FIGS. 51 and 52 Mixed at 1, and heat-treated at 800 ° C and 1 200 ° C using a small desktop electric furnace.
- the appearance photographs of the obtained product are shown in FIGS. 51 and 52, respectively. From FIG. 51, it was found that the appearance of the product heat-treated at 800 ° C. was powdery, and from FIG. 52, the appearance of the product heat-treated at 1 200 ° C. was massive.
- the raw material mixture containing waste Aspest is melted and dissolved at an extremely low temperature as compared with the conventional method, and the needle-like crystal structure of Asbestos rice cake is eliminated and rendered harmless.
- the product is in powder form, zeolite can be produced using raw materials that are easy to handle and have excellent transportability.
- the raw material mixture containing waste asbestos does not contain substances that can be a source of harmful gases, zeolite can be manufactured using raw materials with excellent safety.
- the zeolite obtained by the method for producing the zeolite cake of the present invention has an extremely excellent adsorption ability, and has the ability to adsorb formaldehyde and the like, which are the cause of sick house syndrome, and the moisture conditioning ability and moisture absorption ability.
- FIG. 1 Photo of the used asbestos optical microscope (simple incident polarized light) (Reference Example 1).
- FIG. 2 An electron micrograph of the used asbestos (Reference Example 1).
- FIG. 4 is an electron micrograph of a solid aluminum-containing solid solution obtained from waste asbestos and sodium aluminate (Example 1).
- FIG. 5 is an electron micrograph of the final product obtained from the solid aluminum-containing solid solution of Example 1 (Example 2).
- FIG. 7 is an identification result by a matching peak with a J CPDS card chart by powder X-ray diffraction of the final product of Example 2.
- FIG. 8 is an appearance photograph of the silicon / aluminum-containing solid solution of Example 1 and the final product of Example 2.
- FIG. 9 shows the results of an evaluation test of the adsorption capacity of the final product of Example 2 (Example 3).
- FIG. 10 is an appearance photograph of a silicon / aluminum-containing solid solution obtained at a heat treatment temperature of 700 ° C. (Example 4) and its final product.
- FIG. 11 is a photograph of the appearance of a silicon / aluminum-containing solid solution (Example 4) obtained at a heat treatment temperature of 800 ° C. and its final product.
- FIG. 12 is an appearance photograph of a silicon / aluminum-containing solid solution obtained at a heat treatment temperature of 900 ° C. (Example 4) and its final product.
- FIG. 13 is an electron micrograph of a silicon / aluminum solid solution obtained at a heat treatment temperature of 700 ° C. (Example 4).
- FIG. 14 is an electron micrograph of a silicon / aluminum solid solution obtained at a heat treatment temperature of 800 ° C. (Example 4).
- FIG. 15 is an electron micrograph of a silicon / aluminum solid solution obtained at a heat treatment temperature of 900 ° C. (Example 4).
- FIG. 16 is an electron micrograph of the final product obtained at a heat treatment temperature of 700 ° C. (Example 4).
- FIG. 17 is an electron micrograph of the final product obtained at a heat treatment temperature of 800 ° C. (Example 4).
- FIG. 18 is an electron micrograph of the final product obtained at a heat treatment temperature of 900 ° C. (Example 4).
- FIG. 20 is an electron micrograph of the final product obtained without heating (Example 4).
- FIG. 21 is an electron micrograph of a solid solution obtained with a weight ratio of waste asbestos to sodium aluminate of 2: 1 (Example 5).
- FIG. 22 is an electron micrograph of a solid solution obtained at a weight ratio of waste asbestos to sodium aluminate of 4: 1 (Example 5).
- FIG. 23 is an electron micrograph of a solid solution obtained with a weight ratio of waste asbestos to sodium aluminate of 10: 1 (Example 5).
- FIG. 24 is a result of powder X-ray diffraction of a solid solution obtained at a weight ratio of waste asbestos to sodium aluminate of 2: 1, 4: 1 and 10: 1 (Example 5).
- FIG. 25 is an electron micrograph of the final product obtained with a weight ratio of waste asbestos to sodium aluminate of 2: 1 (Example 5).
- FIG. 26 is an electron micrograph of the final product obtained at a weight ratio of waste asbestos to sodium aluminate of 4: 1 (Example 5).
- FIG. 27 is an electron micrograph of the final product obtained with a weight ratio of waste asbestos to sodium aluminate of 10: 1 (Example 5).
- FIG. 28 is an electron micrograph of a solid aluminum-containing solid solution obtained from waste asbestos and aluminum hydroxide (Example 6).
- FIG. 29 is a result of powder X-ray diffraction of a solid solution containing silicon / aluminum soot obtained from waste asbestos and aluminum hydroxide.
- FIG. 30 is an electron micrograph of a solid aluminum-containing solid solution obtained from waste asbestos and waste aluminum (Example 7).
- FIG. 31 Results of powder X-ray diffraction of solid aluminum-containing solid solution obtained from waste aspaste and waste aluminum.
- FIG. 32 is an electron micrograph of another type of final product obtained from the solid aluminum-containing solid solution (Example 8).
- FIG. 33 shows the result of powder X-ray diffraction of the final product of Example 8.
- FIG. 34 shows the result of identification of the final product of Example 8 by a matching peak with a powdery X-ray diffraction pattern of a JC PDS card.
- FIG. 36 is the result of powder X-ray diffraction of the final product of Example 9.
- FIG. 37 shows the result of identification of the final product of Example 9 by a matching peak with a powdery X-ray diffraction pattern of a JCPDS card.
- FIG. 38 is an electron micrograph of a carbon solid aluminum solution obtained by heat treatment by microwave irradiation (Example 10).
- FIG. 39 is an electron micrograph of the final product obtained by heat treatment using microwave irradiation (Example 10).
- FIG. 40 is a result of powder X-ray diffraction of the final product of Example 10 and Example 2.
- FIG. 41 is an electron micrograph of a silicon-containing solid solution (Example 11).
- FIG. 42 is an electron micrograph of the final product obtained from the silicon-containing solid solution (Example 11).
- FIG. 43 shows the results of powder X-ray diffraction of the final products of Example 1 and Example 2.
- FIG. 45 is an electron micrograph of the final product obtained from the molten slag of Reference Example 2 (Example 12).
- FIG. 46 shows the results of powder X-ray diffraction of the molten slag of Reference Example 2, the final product of Example 12 and the waste base of Reference Example 1.
- FIG. 47 is an electron micrograph of the final product from waste asbestos and sodium aluminate (Comparative Example 1).
- FIG. 48 is an electron micrograph of the final product from the molten slag of waste asbestos (Comparative Example 2).
- FIG. 49 is an electron micrograph of the final product from the molten slag of waste asbestos and waste aluminum (Example 13).
- FIG. 50 is a photograph of the appearance of a detoxified rock-like waste aspaste melt and a powder of this as ground (Example 14).
- FIG. 51 An appearance photograph of a product obtained by mixing sodium aluminate and detoxified waste aspaste melt powder at a weight ratio of 1: 1 and heat-treating at 800 ° C. ( Example 1 4).
- FIG. 52 is an appearance photograph of a product obtained by mixing sodium aluminate and detoxified waste aspaste melt powder at a weight ratio of 1: 1 and heat-treating at 1 200 ° C. (Example 1) Four) .
- FIG. 53 An appearance photograph of a product obtained by mixing calcium silicate and detoxified waste asbestos melt powder at a weight ratio of 1: 1 and heat-treating at 1 200 ° C (Example 1) Four) .
- FIG. 55 is an external appearance photograph of a product obtained by mixing 15% of aluminum oxide with detoxified waste aspaste melt powder and heat-treating it at 1 200 ° C. (Example 14)
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Toxicology (AREA)
- General Health & Medical Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Inorganic Chemistry (AREA)
- Silicates, Zeolites, And Molecular Sieves (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
明 細 書 Specification
廃アスペス卜の無害化処理方法並びにゼォライ卜の製造方法及びそ の製造中間体 Method for detoxifying waste asbestos, method for producing zeoli cake, and production intermediate thereof
技術分野 Technical field
[0001 ] 本発明は、 廃アスベストの無害化処理方法、 並びに廃アスベストを利用し たゼォライ 卜の製造方法、 及びその製造中間体であるケィ素含有固溶体及び ケィ素■アルミニウム含有固溶体に関する。 TECHNICAL FIELD [0001] The present invention relates to a method for detoxifying waste asbestos, a method for producing zeoli cake using waste asbestos, and a silicon-containing solid solution and a key-aluminum-containing solid solution as intermediates for the production.
背景技術 Background art
[0002] アスベストは、 針状結晶構造を有する鉱物繊維であり、 その粉塵を人が吸 い込むと悪性中皮腫等の重篤な疾病を引き起こす。 我が国での 1 9 3 0年か ら 2 0 0 2年の間に消費されたアスペストは 1 0 0 0万トンにも及び、 輸入 アスペス卜の約 9割は建築資材に使用されてきた。 含アスペスト建材が用い られている建造物の解体が今後ピークを迎えることから、 アスペスト暴露と 廃棄処理の問題が深刻化し、 社会問題となっている。 [0002] Asbestos is a mineral fiber having a needle-like crystal structure, and when a person inhales the dust, it causes serious diseases such as malignant mesothelioma. The asbestos consumed in Japan from 1930 to 2000 was 10 million tons, and about 90% of imported Aspes was used for building materials. As demolition of buildings that use Aspest-containing building materials will peak, the problems of Aspest exposure and disposal will become serious and become a social problem.
[0003] また、 アスベストの廃棄処理については、 ほとんどの廃アスベストを、 そ のまま袋詰めにして特別管理廃棄物として最終処分場に埋め立てられている のが現状である。 しかし、 埋め立てによるのみでは、 今後増大が予想される アスペス卜の廃棄量に対応できず、 かつ有害な廃アスペストはそのままの状 態で地中に残ることになり、 将来水災害による流出等で再度環境問題を引き 起こす危険性があった。 かかる問題を解消するため、 最近、 廃アスベストを 無害化し、 他の廃棄物と同様に再資源化して再利用する試みがなされている [0003] Regarding the disposal of asbestos, the present situation is that most waste asbestos is packaged as it is and then landed in a final disposal site as specially managed waste. However, only by landfilling, it will not be possible to cope with the volume of Aspes dredging that is expected to increase in the future, and harmful waste asbestos will remain in the ground as it is. There was a risk of causing environmental problems. In order to solve this problem, recently, attempts have been made to make waste asbestos harmless and to recycle it as other waste.
[0004] 例えば、 アスベスト廃棄物と珪酸カルシウム廃材の処理方法として、 ァス ベストと珪酸カルシウム又はアルミナとを混合し、 1 3 0 0 °C付近の温度で 溶融して無害化する方法 (特許文献 1参照) や、 廃アスベスト材の処理方法 等として、 廃アスベストと酸化アルミとを混合し、 1 2 2 0 °C以上で処理し て無害化し、 窯業製品の原材料として再利用する方法 (特許文献 2参照) 、 及び廃アスペス卜とアルミニウム精鍊時の副生成物であるアルミ ドロスとを 混合し、 8 0 0 °C以上で焼成■粉砕した後に再度 1 2 3 0 °C以上で処理して 無害化し、 窯業製品の原材料として再利用する方法 (特許文献 3参照) が知 られている。 [0004] For example, as a method for treating asbestos waste and calcium silicate waste, asbestos and calcium silicate or alumina are mixed and melted at a temperature around 1300 ° C to make them harmless (Patent Documents) 1) or as a method for treating waste asbestos materials, etc. A method that mixes waste asbestos and aluminum oxide, renders them harmless by treating them at 1 220 ° C or higher, and reuses them as raw materials for ceramic products (Patent Literature) 2) In addition, waste asbestos and aluminum loss, which is a by-product of aluminum smelting, are mixed and fired at 80 ° C or higher. There is known a method of reusing it as a raw material (see Patent Document 3).
[0005] —方、 ゼォライ トは、 結晶中に微細孔を持つアルミノ珪酸塩の総称であり 、 ケィ素とアルミニウムが酸素を介して結合した構造 (S i - 0 - A I - 0 - s i ) を基本骨格とし、 それが三次元的に組合わさることによって形成さ れている。 一般的にゼォライ トは、 ケィ酸ナトリウム溶液とアルミン酸ナト リウム溶液とを混合して焼成■粉砕して製造されるが、 再資源化の一環とし て、 焼却灰、 錶物廃砂、 石炭灰等の可燃性廃棄物を利用してゼォライ トを製 造する方法が検討され (例えば、 特許文献 4及び 5参照) 、 近年実用化され つつある。 [0005] — On the other hand, zeolite is a general term for aluminosilicates with fine pores in the crystal, and has a structure (S i-0-AI-0-si) in which silicon and aluminum are bonded via oxygen. The basic skeleton is formed by three-dimensional combination. Zeolite is generally manufactured by mixing and firing sodium silicate and sodium aluminate solutions. ■ As part of recycling, incineration ash, waste waste sand, coal ash A method for producing zeolite using combustible wastes such as the above has been studied (see, for example, Patent Documents 4 and 5), and has recently been put into practical use.
特許文献 1 :特開平 4 _ 1 8 0 8 7 9号公報 Patent Document 1: Japanese Patent Application Laid-Open No. 4 _ 1 8 8 7 9
特許文献 2:特開平 5— 1 3 8 1 4 7号公報 Patent Document 2: JP-A-5-1 3 8 1 4 7
特許文献 3:特開平 6— 1 3 4 4 3 8号公報 Patent Document 3: Japanese Patent Laid-Open No. 6-1 3 4 4 3 8
特許文献 4:特開平 1 1— 1 9 9 2 2 5号公報 Patent Document 4: Japanese Patent Laid-Open No. 1 1-1 9 9 2 2 5
特許文献 5:特開 2 0 0 0 _ 1 5 9 5 1 7号公報 Patent Document 5: Japanese Patent Laid-Open No. 2 00 0 _ 1 5 9 5 1 7
発明の開示 Disclosure of the invention
発明が解決しょうとする課題 Problems to be solved by the invention
[0006] しかしながら、 廃アスペストを再利用してゼォライ トを製造する方法につ いては知られていない。 [0006] However, there is no known method for producing zeolite by reusing waste asbestos.
[0007] また、 文献 1及び 2に開示されている廃アスベストの無害化方法では、 珪 酸カルシウム廃材や酸化アルミニウムを溶融点降下物質として添加しても、 1 2 0 0 °C以上の温度で溶融する必要があるので、 高温溶融炉設備や安全管 理等への経済的負担が増加するという問題が生じていた。 また、 上記の無害 化方法によって得られる生成物は硬い岩石状であるので、 これをゼォライ ト の原材料として用いる場合には、 運搬性に問題があり、 さらに運搬しやすい ように粉砕すると製造工程が増えてコスト性も問題になるので、 好ましくな い。 [0007] Further, in the method for detoxifying waste asbestos disclosed in Documents 1 and 2, even if calcium silicate waste material or aluminum oxide is added as a melting point depressant, the temperature is not lower than 120 ° C. Since melting is necessary, there has been a problem that the economic burden on the high-temperature melting furnace facilities and safety management increases. In addition, the product obtained by the above detoxification method is hard rock-like, so when using it as a raw material for zeolite, there is a problem in transportability, and if it is pulverized so that it can be transported more easily, the manufacturing process is reduced. Increased cost becomes a problem, so it is preferable Yes.
[0008] さらに、 文献 3に開示されている廃アスベストの再利用方法では、 アルミ ニゥ厶精鍊時の副生成物であるアルミ ドロスを用いているが、 このアルミ ド ロスには金属アルミニウムが含有されており、 ゼォライ 卜の製造に必要なァ ルカリ処理において、 水素ガスを発生して爆発を起こすので、 ゼォライ 卜の 原材料として利用することができなかった。 [0008] Furthermore, in the method for recycling waste asbestos disclosed in Reference 3, aluminum dross, which is a by-product during the milling of aluminum, is used, and this aluminum loss contains metallic aluminum. In the alkaline treatment necessary for the production of Zeora, hydrogen gas was generated and caused an explosion, so it could not be used as a raw material for Zerai.
[0009] 従って、 本発明の目的は、 無害化した廃アスベストを利用したゼォライ ト の製造方法、 及びその製造中間体を提供することにある。 [0009] Accordingly, an object of the present invention is to provide a method for producing zeolite using detoxified waste asbestos, and a production intermediate thereof.
[0010] また、 本発明の他の目的は、 低コストで簡便かつ安全に再利用可能なゼォ ライ 卜の製造方法、 及びその製造中間体を提供することにある。 [0010] In addition, another object of the present invention is to provide a method for producing zeolite candy that can be easily and safely reused at low cost, and a production intermediate thereof.
[001 1 ] また、 本発明の他の目的は、 有害な廃アスベストを簡便かつ低コストで無 害化処理する方法を提供することにある。 [001 1] Another object of the present invention is to provide a method for detoxifying harmful waste asbestos simply and at low cost.
課題を解決するための手段 Means for solving the problem
[0012] 本願発明者は、 斯かる従来技術の問題点に鑑み、 ゼォライ 卜の原材料につ いて鋭意研究を重ねた結果、 所定条件下で得られる廃アスペスト固溶体が、 ゼォライ 卜の原材料の代替として用いることが極めて有用であることを見出 し、 本発明を完成した。 [0012] In view of the problems of the prior art, the inventor of the present application has conducted intensive research on the raw materials of Zeora coffee, and as a result, the waste asbestos solid solution obtained under the predetermined conditions is used as an alternative to the raw material of Zerai coffee. It was found that it was very useful to use, and the present invention was completed.
[0013] ( 1 ) すなわち、 本発明は、 廃アスベストとアルミン酸又はその塩とを混 合した後、 7 0 0〜 1 0 0 0 °Cで加熱処理してケィ素■アルミニウム含有固 溶体とすることを特徴とする、 廃アスペス卜の無害化処理方法である。 [0013] (1) That is, in the present invention, waste asbestos and aluminate or a salt thereof are mixed and then heat-treated at 70 to 100 ° C. to obtain a carbon-aluminum-containing solid solution. This is a detoxification method for waste asbestos.
[0014] ( 2 ) また、 本発明は、 廃アスベストとケィ素含有物質を混合した後、 7 0 0〜 1 0 0 0 °Cで加熱処理してケィ素含有固溶体とすることを特徴とする 、 廃アスペス卜の無害化処理方法である。 [0014] (2) Further, the present invention is characterized in that waste asbestos and a silicon-containing substance are mixed and then heat-treated at 70 ° C to 100 ° C to obtain a silicon-containing solid solution. This is a detoxification method for waste Aspes.
[0015] ( 3 ) また、 本発明は、 アスベストとアルミニウム含有物質とを混合した 後加熱処理してケィ素■アルミニウム含有固溶体とし、 次いで前記ケィ素■ アルミニウム含有固溶体をアルカリ処理することを特徴とする、 ゼォライ ト の製造方法である。 [0015] (3) Further, the present invention is characterized in that asbestos and an aluminum-containing substance are mixed and then heat-treated to form a carbon / aluminum-containing solid solution, and then the alkali / aluminum-containing solid solution is alkali-treated. This is a method for producing zeolite.
[001 6] ( 4 ) また、 本発明は、 前記アルミニウム含有物質が、 アルミン酸又はそ の塩であることを特徴とする、 (3) に記載のゼォライ トの製造方法である [001 6] (4) In the present invention, the aluminum-containing substance may be aluminate or The method for producing a zeolite according to (3), characterized in that it is a salt of
[0017] (5) また、 本発明は、 前記加熱処理が、 700°C以上で行われることを 特徴とする、 (3) に記載のゼォライ トの製造方法である。 [0017] (5) Further, the present invention is the method for producing a zeolite according to (3), wherein the heat treatment is performed at 700 ° C or higher.
[0018] (6) また、 本発明は、 前記加熱処理が、 700〜1 000°Cで行われる ことを特徴とする、 (3) に記載のゼォライ トの製造方法である。 [0018] (6) Moreover, the present invention is the method for producing a zeolite according to (3), wherein the heat treatment is performed at 700 to 1,000 ° C.
[0019] (7) また、 本発明は、 アスベストとケィ素含有物質とを混合した後加熱 処理してケィ素含有固溶体とし、 次いで前記ケィ素含有固溶体とアルミニゥ ム含有物質とを混合した後アルカリ処理することを特徴とする、 ゼォライ ト の製造方法である。 [0019] (7) Further, in the present invention, asbestos and a silicon-containing substance are mixed and then heat-treated to obtain a silicon-containing solid solution, and then the alkali-containing substance is mixed with the silicon-containing solid solution and the alkali-containing substance. A method for producing zeolite.
[0020] (8) また、 本発明は、 前記ケィ素含有物質はケィ酸又はその塩であり、 前記アルミニウム含有物質はアルミン酸又はその塩であることを特徴とする [0020] (8) Further, the present invention is characterized in that the above-mentioned key substance-containing substance is a key acid or a salt thereof, and the above-mentioned aluminum-containing substance is an aluminate or a salt thereof.
、 (7) に記載のゼォライ トの製造方法である。 (7) A method for producing zeolite.
[0021] (9) また、 本発明は、 前記加熱処理が、 700°C以上で行われることを 特徴とする、 (7) に記載のゼォライ トの製造方法である。 [0021] (9) Further, the present invention is the method for producing a zeolite according to (7), wherein the heat treatment is performed at 700 ° C or higher.
[0022] (1 0) また、 本発明は、 前記加熱処理が、 700~1 000°Cで行われ ることを特徴とする、 (7) に記載のゼォライ トの製造方法である。 [0022] (10) Further, the present invention provides the method for producing a zeolite according to (7), wherein the heat treatment is performed at 700 to 1,000 ° C.
[0023] (1 1 ) また、 本発明は、 アスベストを加熱処理して溶融スラグとし、 次 いで前記溶融スラグとアルミニウム含有物質とを混合した後アル力リ処理す ることを特徴とする、 ゼォライ 卜の製造方法である。 [0023] (11) Further, the present invention is characterized in that asbestos is heat-treated to form molten slag, and then the molten slag and the aluminum-containing material are mixed and then subjected to an al force treatment. It is a manufacturing method of a kite.
[0024] ( 1 2) また、 本発明は、 アスベストとアルミン酸又はその塩とを混合し た後、 700〜 1 000°Cで加熱処理して得られることを特徴とする、 ケィ 素■アルミニウム含有固溶体である。 [0024] (12) The present invention is also characterized in that it is obtained by mixing asbestos and aluminate or a salt thereof, and then heat-treating at 700 to 1 000 ° C. It is a contained solid solution.
[0025] (1 3) また、 本発明は、 アスベストとアルミン酸又はその塩とを混合し た後、 800〜 900°Cで加熱処理して得られることを特徴とする、 ケィ素 ■アルミニウム含有固溶体である。 [0025] (1 3) Further, the present invention is characterized in that it is obtained by mixing asbestos and aluminate or a salt thereof and then heat-treating at 800 to 900 ° C. It is a solid solution.
[0026] (1 4) また、 本発明は、 アスベストとケィ素含有物質とを混合した後、 [0026] (1 4) Further, in the present invention, after mixing the asbestos and the silicon-containing substance,
700〜1 000°Cで加熱処理して得られることを特徴とする、 ケィ素含有 固溶体である。 Contains silicon, obtained by heat treatment at 700 to 1 000 ° C It is a solid solution.
[0027] ( 1 5 ) また、 本発明は、 アスベストとケィ素含有物質とを混合した後、 [0027] (15) In the present invention, after mixing asbestos and a substance containing silicon,
8 0 0 - 9 0 0 °Cで加熱処理して得られることを特徴とする、 ケィ素含有固 溶体である。 It is a silicon-containing solid solution obtained by heat treatment at 800-900 ° C.
[0028] ( 1 6 ) さらに、 本発明は、 前記ケィ素含有物質は、 ケィ酸又はその塩で あることを特徴とする、 (1 4 ) 又は (1 5 ) に記載のケィ素含有固溶体で あ^ ο [0028] (16) Further, the present invention provides the silicon-containing solid solution as described in (14) or (15), wherein the key substance is a key acid or a salt thereof. Oh ^ ο
[0029] 上記手段によれば、 以下のような作用が得られる。 [0029] According to the above means, the following operation is obtained.
発明の効果 The invention's effect
[0030] 本発明のゼォライ 卜の製造方法によれば、 従来法に比べて極めて低温で廃 アスペストを含む原料混合物を溶融固溶化し、 アスペス卜の針状結晶構造を 消失させ無害化することができるので、 経済的負担をかけることなく、 それ を有効に再利用して簡易にゼォライ トを製造することができる。 [0030] According to the method for producing zeoli cake of the present invention, the raw material mixture containing waste asbestos can be melted and solidified at an extremely low temperature compared to the conventional method, and the needle-like crystal structure of the asbestos cake can be eliminated and rendered harmless. As a result, it is possible to manufacture zeolite easily by effectively reusing it without imposing an economic burden.
[0031 ] また、 本発明のゼォライ 卜の製造方法によれば、 従来法に比べて極めて低 温で廃アスペストを無害化することができ、 その生成物が粉末状であるので 、 取り扱いが容易で運搬性に優れた原材料を用いてゼォライ トを製造するこ とができる。 [0031] In addition, according to the method for producing zeoli rice cake of the present invention, waste asbestos can be rendered harmless at an extremely low temperature as compared with the conventional method, and the product is in powder form, so that it is easy to handle. Zeolite can be manufactured using raw materials with excellent transportability.
[0032] さらに、 本発明のゼォライ 卜の製造方法によれば、 従来法に比べて極めて 低温で廃アスペストを無害化することができ、 かつ廃アスペストを含む原料 混合物中に有害ガスの発生源となり得る物質を含まないので、 安全性に優れ た原材料を用いてゼォライ トを製造することができる。 [0032] Further, according to the method for producing zeoli rice cake of the present invention, waste asbestos can be rendered harmless at an extremely low temperature as compared with the conventional method, and it becomes a source of harmful gas in the raw material mixture containing waste asbestos. Because it does not contain any substances that can be obtained, zeolite can be manufactured using highly safe raw materials.
発明を実施するための最良の形態 BEST MODE FOR CARRYING OUT THE INVENTION
[0033] 以下、 本発明の実施の形態を説明する。 Hereinafter, embodiments of the present invention will be described.
[0034] 本発明の第 1の実施形態は、 アスベストとアルミニウム含有物質とを混合 した後加熱処理してケィ素■アルミニウム含有固溶体とし、 次いで前記ケィ 素■アルミニウム含有固溶体をアル力リ処理することを特徴とするゼォライ 卜の製造方法である。 [0034] In the first embodiment of the present invention, asbestos and an aluminum-containing substance are mixed and then heat-treated to form a carbon-aluminum-containing solid solution, and then the silicon-aluminum-containing solid solution is subjected to an aluminum force treatment. This is a method for producing zeoli rice cake.
[0035] 本実施形態のゼォライ 卜の製造に用いられるアスペストは特に限定される ものではなく、 蛇紋石族のクリソタイル (温石綿■ 白石綿、 Mg6S i 4O10 (OH) 8) 、 角閃石族のクロシドライ ト (青石綿、 N a2 (F e 2 + >M g) 3 (F e 3+) 2S i 8022 (OH) 2) 、 ァモサイ ト ( (Mg<F e2 + ) 7S i 8 022 (OH) 2) 、 アンソフイライ ト ( (Mg>F e2 + ) 7S i 8022 (OH ) 2) 、 トレモライ ト(Ca2Mg5S i 8022 (OH) 2) 、 ァクチノライ ト ( Ca2 (Mg, F e 2 + ) 5S i 8022 (OH) 2) 等の各種アスペストを含有す る廃棄物を無害化処理することが可能である。 [0035] The asbestos used in the production of the zeorai rice cake of the present embodiment is particularly limited. Serinolite chrysotile (spar asbestos ■ Mg 6 S i 4 O 10 (OH) 8 ), amphibolite crosilite (Ao Asbestos, Na 2 (F e 2 + > M g ) 3 (F e 3+ ) 2 Si 8 0 22 (OH) 2 ), Amosite ((Mg <F e 2 + ) 7 Si 8 0 22 (OH) 2 ), Anthophyllite ((Mg> F e 2 + ) 7 S i 8 0 22 (OH) 2 ), tremolite (Ca 2 Mg 5 S i 8 0 22 (OH) 2 ), actinolite (Ca 2 (Mg, F e 2 +) 5 S i It is possible to detoxify waste containing various asbestos such as 8 0 22 (OH) 2 ).
[0036] 本実施形態で利用されるアルミニウム含有物質は、 ゼォライ 卜の原材料と なり得るものであって、 水素ガスを発生させなければ特に限定されるもので はなく、 例えば、 アルミン酸エステル、 アランダム、 τ—アルミナ、 一ァ ルミナ等の酸化アルミニウム、 水酸化アルミニウム、 アルミン酸、 アルミン 酸ナトリウム、 アルミン酸カリウム、 アルミン酸カルシウム、 アルミン酸コ バルト、 アルミン酸ストロンチウム、 アルミン酸バリウム、 アルミン酸ベリ リゥ厶、 アルミン酸マグネシウム等のアルミン酸塩等を単独でまたは 2種以 上を組み合わせて用いることができる。 これらの中では、 アルミン酸又はそ の塩が好ましく、 本発明においては、 アルミン酸ナトリゥ厶が好適に利用さ れる。 [0036] The aluminum-containing material used in the present embodiment is a material that can be used as a raw material for zeoli cake, and is not particularly limited as long as it does not generate hydrogen gas. Random, τ-alumina, aluminum oxide such as alumina, aluminum hydroxide, aluminate, sodium aluminate, potassium aluminate, calcium aluminate, cobalt aluminate, strontium aluminate, barium aluminate, beryllium aluminateア ル ミ, Aluminates such as magnesium aluminate can be used alone or in combination of two or more. Of these, aluminate or a salt thereof is preferable, and sodium aluminate is preferably used in the present invention.
[0037] 本実施形態にかかるゼォライ 卜の製造方法では、 まず、 廃アスベストとァ ルミニゥ厶含有物質をよく混合する。 廃アスベストとアルミニウム含有物質 の混合比率は、 原料中のケィ素とアルミニウムのモル比が 1 0 : 1 ~1 : 4 、 好ましくは 2 : 1 ~1 : 2となる範囲である。 原料の混合方法としては、 混合機や粉砕機等を利用して直接原料を粉砕混合する方法や水等の溶媒を用 いて原料を溶解、 懸濁等させ撹拌混合する方法等が挙げられるが、 特に限定 されるものではない。 [0037] In the method for producing zeoli cake according to this embodiment, first, waste asbestos and aluminium-containing material are mixed well. The mixing ratio of the waste asbestos and the aluminum-containing substance is in a range in which the molar ratio of silicon to aluminum in the raw material is 10: 1 to 1: 4, preferably 2: 1 to 1: 2. Examples of the raw material mixing method include a method of directly pulverizing and mixing the raw material using a mixer, a pulverizer, etc., a method of dissolving and suspending the raw material using a solvent such as water, and stirring and mixing. There is no particular limitation.
[0038] 次に、 得られた廃アスベストとアルミニウム含有物質の混合物を加熱処理 する。 加熱処理の方法としては、 電気炉による方法、 マイクロウエーブ照射 による方法、 マイクロ波、 高周波、 低周波、 マイクロプラズマ、 高周波ブラ ズマ等を利用する方法等が挙げられる。 これらの中では、 処理時間の短縮化 や装置の小型化の観点から、 電気炉による方法が特に好ましい。 [0038] Next, the obtained mixture of waste asbestos and aluminum-containing material is heat-treated. Examples of the heat treatment method include a method using an electric furnace, a method using microwave irradiation, a method using a microwave, a high frequency, a low frequency, a microplasma, a high frequency plasma, and the like. Among these, shortening of processing time The method using an electric furnace is particularly preferable from the viewpoint of downsizing the apparatus.
[0039] また、 加熱処理の温度は、 100°C以上、 好ましくは 700°C~ 1 000 °Cの範囲であり、 さらに好ましくは 800°C~900°Cの範囲である。 処理 温度が 700°C未満では、 アスペス卜の針状結晶構造が残存し完全な無害化 が図れず、 1 000°C以上では、 無害化が達成され、 これ以上処理温度を上 げることはかえつてコスト高を招くからである。 さらに、 生成したケィ素 - アルミニウム含有固溶体は硬い岩石状であるので粉砕が必要となり、 製造ェ 程が煩雑になるので好ましくない。 ここで、 アスベスト単独の溶融温度は約 1 500°Cである。 従って、 廃アスベストを単独で加熱処理して無害化する 従来法に比べ、 本発明の方法によれば、 極めて低温で廃アスベストを含む原 料混合物を溶融固溶化し、 アスペス卜の針状結晶構造を消失させ無害化する ことができるので、 無害化処理の低コスト化を図ることができる。 なお、 処 理時間は、 前記処理温度で原料混合物が溶融固溶化するのに十分な時間であ り、 処理温度及び原料混合物の量により適宜決定される。 [0039] The temperature of the heat treatment is 100 ° C or higher, preferably in the range of 700 ° C to 1 000 ° C, and more preferably in the range of 800 ° C to 900 ° C. If the processing temperature is less than 700 ° C, the needle-like crystal structure of Aspes 残存 remains and cannot be completely detoxified, and if it exceeds 1 000 ° C, detoxification is achieved and the processing temperature cannot be further increased. This is because the cost increases. Furthermore, since the formed silicon-aluminum-containing solid solution is hard and rocky, it needs to be pulverized, and the manufacturing process becomes complicated, which is not preferable. Here, the melting temperature of asbestos alone is about 1500 ° C. Therefore, compared to the conventional method in which waste asbestos is heat-treated and made harmless, according to the method of the present invention, the raw material mixture containing waste asbestos is melted and dissolved at an extremely low temperature, and the needle-like crystal structure of Aspes Can be eliminated and rendered harmless, so the cost of the harmless treatment can be reduced. The treatment time is a time sufficient for the raw material mixture to melt and dissolve at the treatment temperature, and is appropriately determined depending on the treatment temperature and the amount of the raw material mixture.
[0040] 本実施形態の製造方法では、 加熱処理後冷却固化して得られたケィ素■ァ ルミニゥ厶含有固溶体に対してアル力リ処理を施してゼォライ トを生成する 。 アルカリ処理に用いるアルカリとしては、 水酸化ナトリウム、 水酸化カリ ゥ厶、 水酸化カルシウム等が挙げられるが、 特にこれに限定されるものでは ない。 処理条件は、 常圧では、 アルカリ濃度が 0. 5~5 N、 好ましくは 1 . 5~3. 5 N、 処理温度が 80~ 1 00°C、 好ましくは 90~95°C、 処 理時間が 0. 5~48時間、 好ましくは 1 ~24時間である。 なお、 アル力 リ処理は、 1〜5 a t m、 好ましくは 1. 25〜 2 a t mの加圧下で行って もよく、 その場合のアルカリ濃度は 0. 5〜51\1、 好まし<は1. 5〜3. 5 N、 処理温度は 1 20〜 230°C、 好ましくは 1 30〜 1 50°C、 処理時 間は 0. 5〜24時間、 好ましくは 1〜 1 0時間である。 これらの処理条件 が上記下限未満では十分なゼォライ ト化が得られず、 上記上限を超えると、 過剰条件となり容器を損傷する等の弊害を招くので好ましくない。 [0040] In the manufacturing method of the present embodiment, zeolite is generated by subjecting a key alloy-containing solid solution obtained by cooling and solidification after heat treatment to an Al force treatment. Examples of the alkali used for the alkali treatment include sodium hydroxide, potassium hydroxide, calcium hydroxide and the like, but are not particularly limited thereto. Treatment conditions are as follows: At normal pressure, alkali concentration is 0.5 to 5 N, preferably 1.5 to 3.5 N, treatment temperature is 80 to 100 ° C, preferably 90 to 95 ° C, treatment time Is 0.5 to 48 hours, preferably 1 to 24 hours. In addition, the Al force treatment may be performed under a pressure of 1 to 5 atm, preferably 1.25 to 2 atm, in which case the alkali concentration is 0.5 to 51 \ 1, preferably <1. 5 to 3.5 N, treatment temperature is 120 to 230 ° C, preferably 130 to 150 ° C, and treatment time is 0.5 to 24 hours, preferably 1 to 10 hours. If these treatment conditions are less than the above lower limit, sufficient gelation cannot be obtained, and if the above upper limit is exceeded, excessive conditions will be caused, which may cause adverse effects such as damage to the container.
[0041] 上記アル力リ処理で得られた生成物をろ過または遠心分離等により取得し 乾燥することにより、 目的のゼォライ トが得られる。 [0041] The product obtained by the above-described Al force treatment is obtained by filtration or centrifugation. By drying, the desired zeolite can be obtained.
[0042] 本発明の第 2の実施形態は、 アスベストとケィ素含有物質とを混合した後 加熱処理してケィ素含有固溶体とし、 次いで前記ケィ素含有固溶体とアルミ ニゥム含有物質とを混合した後アル力リ処理することを特徴とするゼォライ 卜の製造方法である。 [0042] In the second embodiment of the present invention, after mixing asbestos and a silicon-containing material, heat treatment is performed to obtain a silicon-containing solid solution, and then, the above-mentioned silicon-containing solid solution and the aluminum-containing material are mixed. This is a method for producing zeoli rice cake, which is characterized in that it is treated with an al force.
[0043] 本実施形態で利用されるケィ素含有物質は、 ケィ素を含有する物質であれ ば特に限定されるものではなく、 例えば、 ケィ酸ナトリウム、 ケィ酸力リウ ム等のケィ酸塩、 ケィ酸硝子、 ソーダ石灰硝子、 カリ石灰硝子等のケィ酸塩 硝子、 珪藻土、 カオリン、 メタカオリン等が挙げられ、 これらを単独でまた は 2種以上を組み合わせて用いることができる。 これらの中では、 ケィ酸又 はその塩が好ましく、 本発明においては、 ケィ酸ナトリウムが好適に利用さ れる。 [0043] The key-containing substance used in the present embodiment is not particularly limited as long as it is a key-containing substance. For example, a sodium salt, a key salt such as sodium key acid, Examples thereof include silicate glass such as kainate glass, soda lime glass, potash lime glass, diatomaceous earth, kaolin, and metakaolin, and these can be used alone or in combination of two or more. Of these, kaic acid or a salt thereof is preferable, and sodium kaate is preferably used in the present invention.
[0044] なお、 本実施形態で利用される原料の廃アスベスト、 アルミニウム含有物 質、 原料の混合方法、 加熱処理の方法、 温度、 時間等は、 前記第 1の実施形 態における場合と同様である。 [0044] The raw material waste asbestos, the aluminum-containing material, the raw material mixing method, the heat treatment method, the temperature, the time, etc. used in the present embodiment are the same as those in the first embodiment. is there.
[0045] 本実施形態の製造方法では、 加熱処理後冷却固化して得られたケィ素含有 固溶体にアルミニウム含有物質を混合し、 得られた混合物をアル力リ処理す ることによリゼオラィ トを生成する。 ケィ素含有固溶体とアルミニウム含有 物質の混合比率は、 原料中のケィ素とアルミニウムのモル比が 1 0 : 1 ~ 1 : 4、 好ましくは 2 : 1 ~ 1 : 2となる範囲である。 混合方法、 アルカリ処 理の方法及び条件等は前記前記第 1の実施形態における場合と同様である。 [0045] In the production method of the present embodiment, an aluminum-containing substance is mixed with the silicon-containing solid solution obtained by cooling and solidifying after the heat treatment, and the resulting mixture is subjected to al force retreatment to obtain a lysate. Generate. The mixing ratio of the silicon-containing solid solution and the aluminum-containing substance is such that the molar ratio of the silicon and the aluminum in the raw material is 10: 1 to 1: 4, preferably 2: 1 to 1: 2. The mixing method, alkali treatment method, conditions, and the like are the same as those in the first embodiment.
[0046] 本発明の第 3の実施形態は、 アスベストを加熱処理して溶融スラグとし、 次いで前記溶融スラグとアルミニウム含有物質とを混合した後アル力リ処理 することを特徴とするゼォライ 卜の製造方法である。 [0046] In a third embodiment of the present invention, the asbestos is produced by heat-treating asbestos into molten slag, then mixing the molten slag and the aluminum-containing substance, and then subjecting to asphalt treatment. Is the method.
[0047] 本実施形態で利用されるアスベスト及びアルミニウム含有物質は、 前記第 [0047] The asbestos and aluminum-containing material used in the present embodiment is
1の実施形態におけるものと同様である。 The same as in the first embodiment.
[0048] 本実施形態の製造方法では、 まず、 アスベストを約 1 5 0 0 °Cで加熱処理 して溶融スラグとする。 加熱処理の方法及び条件等は前記第 1の実施形態に おける場合と同様である。 ついで、 溶融スラグとアルミニウム含有物質を混 合し、 得られた混合物をアルカリ処理してゼォライ トを得る。 原料の混合方 法、 アル力リ処理の方法及び条件等は前記第 1の実施形態における場合と同 様である。 [0048] In the manufacturing method of the present embodiment, first, asbestos is heat-treated at about 150 ° C to obtain molten slag. The heat treatment method and conditions are the same as those in the first embodiment. It is the same as the case where it can be placed. Next, molten slag and an aluminum-containing material are mixed, and the resulting mixture is alkali-treated to obtain zeolite. The method of mixing the raw materials, the method and conditions of the power treatment, etc. are the same as those in the first embodiment.
[0049] 本発明の製造方法では、 原料中のケィ素とアルミニウムの比率、 アルカリ 処理の圧力等の諸条件を適宜調整することにより、 ソーダライ ト、 ゼォライ h A、 ゼォライ ト P等の各種ゼォライ トを製造することができる。 [0049] In the production method of the present invention, various zeolites such as sodalite, zeolite hA, zeolite p, and the like are adjusted by appropriately adjusting various conditions such as the ratio of silicon to aluminum in the raw material and the pressure of the alkali treatment. Can be manufactured.
[0050] 本発明の第四の実施形態は、 アスベストとケィ素含有物質とを混合した後 、 7 0 0〜1 0 0 0 °Cで加熱処理して得られることを特徴とするケィ素含有 固溶体である。 [0050] A fourth embodiment of the present invention is obtained by mixing asbestos and a silicon-containing substance and then heat-treating at 700 to 100 ° C. It is a solid solution.
[0051 ] 本実施形態のケィ素含有固溶体の製造方法は、 前記第二の実施形態におけ る場合と同様である。 [0051] The method for producing the silicon-containing solid solution of the present embodiment is the same as that in the second embodiment.
[0052] 本発明の第五の実施形態は、 アスベストとアルミン酸ナトリウムとを混合 した後、 7 0 0 ~ 1 0 0 0 °Cで加熱処理して得られるケィ素■アルミニウム 含有固溶体である。 A fifth embodiment of the present invention is a silicon / aluminum-containing solid solution obtained by mixing asbestos and sodium aluminate, followed by heat treatment at 700 to 100 ° C.
[0053] 本実施形態のケィ素■アルミニウム含有固溶体の製造方法は、 前記第一の 実施形態における場合と同様である。 [0053] The method for producing the silicon-aluminum-containing solid solution of the present embodiment is the same as in the first embodiment.
[0054] 本発明のケィ素含有固溶体及びケィ素■アルミニウム含有固溶体を用いる ことにより、 ことにより、 前記各種ゼォライ トを製造することができる。 実施例 [0054] By using the silicon-containing solid solution and the silicon-aluminum-containing solid solution of the present invention, the various zeolites can be produced. Example
[0055] 次に、 本発明の無害化廃アスペストを用いたゼォライ 卜の製造方法及びそ の製造中間体を、 実施例によりさらに詳細に説明するが、 これは本発明の実 施態様を例示したものであり、 本発明はこれらの実施例に限定されるもので はない。 よって、 本発明の要旨を逸脱しない範囲内において種々変更を加え 得ることは勿論である。 [0055] Next, the method for producing zeorai koji using the detoxification waste asbestos of the present invention and the production intermediate thereof will be described in more detail by way of examples, which illustrate the embodiment of the present invention. However, the present invention is not limited to these examples. Therefore, it goes without saying that various modifications can be made without departing from the scope of the present invention.
[0056] なお、 以下の実験は、 特に明記したものを除き下記の機器及び条件ならび に試薬を用いて行った。 [0056] The following experiments were performed using the following equipment, conditions, and reagents, except as otherwise specified.
( 1 ) 測定機器 (a) 粉末 X線回折装置 (リガク社製 R I NT 2200— V型) 、 倍率: 2 00倍 (1) Measuring equipment (a) Powder X-ray diffractometer (RI NT 2200—V type, manufactured by Rigaku Corporation), magnification: 200 times
(b) 電子顕微鏡 (日立製作所社製 S_21 50型又は日本電子株式会社製 J SM- 6330 F) 、 倍率: 4000倍 (b) Electron microscope (Hitachi S_21 50 type or JEOL J SM-6330 F), magnification: 4000 times
(2) 加熱機器 (2) Heating equipment
(a) 無酸化雰囲気焼入炉 (サーマル社製 SAD 330型) 、 使用温度: 6 00〜 1 060°C、 加熱炉有効寸法: 027 O X H 2 OO、 処理量: 25 k g/g r o s s (治具■ トレー含む) 、 油槽:約 250リツトル、 窒素気流 下で実施 (a) Non-oxidizing atmosphere quenching furnace (Thermal SAD 330 type), Operating temperature: 600-1060 ° C, Heating furnace effective dimension: 027 OXH 2 OO, Processing amount: 25 kg / gross (Jig ■ (Including tray) Oil tank: Approximately 250 liters, conducted under nitrogen flow
(b) 高温電気炉 (ネムス社製 B4S— 1 Z 1 0_ 1 7型) 、 有効炉内寸法 : 300WX 300WX 350 H 温度コントローラー付、 ヒーター:スー パーカンタル 1 800 X 1 0本、 大気中で実施 (b) High-temperature electric furnace (Nems B4S— 1 Z 1 0_ 17 type), effective furnace dimensions: 300WX 300WX 350 H with temperature controller, heater: Supercantal 1 800 X 10 pieces, conducted in air
(c) 卓上小型電気炉 (曰陶科学株式会社製 NHK— 1 70型) 、 使用温度 : 800-1 200°C (c) Desktop small-sized electric furnace (NHK-1 70 type, manufactured by Sakai Ceramics Co., Ltd.), operating temperature: 800-1 200 ° C
(3) 試薬 (3) Reagent
(a) アルミン酸ナトリウム (和光純薬工業製 試薬 1級) (a) Sodium aluminate (Wako Pure Chemical Industries, reagent grade 1)
(b) 水酸化ナトリウム (東ソー製 「トーソパール」 、 水酸化ナトリウム 9 9%) (b) Sodium hydroxide (Tosoh Pearl manufactured by Tosoh Corporation, 9% sodium hydroxide)
(c) ケィ酸カルシウム (和光純薬工業製 試薬 1級) (c) Calcium silicate (Reagent grade 1 manufactured by Wako Pure Chemical Industries)
(d) 酸化アルミニウム (和光純薬工業製 試薬特級) (d) Aluminum oxide (special grade reagent manufactured by Wako Pure Chemical Industries)
[0057] [参考例 1 ] 廃アスペス卜の分析 [0057] [Reference Example 1] Analysis of waste asbestos
[0058] 使用した廃アスベストの光学顕微鏡 (落射簡易偏光) 写真及び電子顕微鏡 写真を、 それぞれ図 1及び図 2に示した。 また、 使用した廃アスベストの粉 末 X線回折による J CPDSカードチャートとのマッチングピークによる同 定結果を、 図 3に示した。 [0058] An optical microscope (simple incident polarization) photograph and an electron microscope photograph of the waste asbestos used are shown in FIGS. 1 and 2, respectively. Figure 3 shows the results of the identification of matching peaks with the J CPDS card chart of the used asbestos powder X-ray diffraction.
[0059] 図 1及び図 2より、 使用した廃アスベストは、 有害とされるアスベストに 特有の針状の結晶構造が認められた。 また、 図 3より、 使用した廃アスペス トは、 アンソフィライ ト (融点 1 468°C) とクロシドライ ト (融点 1 1 9 3°C) の混合物にァモサイ ト (融点 1 397°C) がわずかに混じったもので あることがわかった。 [0059] From Fig. 1 and Fig. 2, it was confirmed that the used asbestos had a needle-like crystal structure peculiar to harmful asbestos. In addition, according to Fig. 3, the waste asperities used were anisophyllite (melting point 1 468 ° C) and crosidite (melting point 1 1 9 It was found that the mixture at 3 ° C was slightly mixed with amosite (melting point 1 397 ° C).
[0060] [実施例 1 ] 廃アスベストとアルミン酸ナトリウムからのケィ素■アルミ ニゥム含有固溶体の調製 [Example 1] Clay from waste asbestos and sodium aluminate ■ Preparation of solid solution containing aluminum
[0061] 参考例 1の廃アスペスト 1 00 gとアルミン酸ナトリウム 1 00 gに水 2 50m I を加えてよく混合し、 水分を蒸発させて廃アスペス卜とアルミン酸 ナトリゥムの混合物とした。 得られた混合物 1 0 gを無酸化雰囲気焼入炉で 、 1 000°C、 1時間加熱後冷却して、 ケィ素■アルミニウム含有固溶体 5 . 7 gを得た。 得られた固溶体の電子顕微鏡写真を図 4に、 粉末 X線回折の 結果を図 6 (a) に、 及び外観写真を図 8 (a) にそれぞれ示した。 なお、 比較のため、 参考例 1の廃アスベストの粉末 X線回折の結果を図 6 (c) に 示した。 [0061] To 100 g of the waste asbestos of Reference Example 1 and 100 g of sodium aluminate, 250 ml of water was added and mixed well, and the water was evaporated to obtain a mixture of waste asbestos and sodium aluminate. The obtained mixture (10 g) was heated in a non-oxidizing atmosphere quenching furnace at 1 000 ° C. for 1 hour and then cooled to obtain 5.7 g of silicon / aluminum-containing solid solution. Fig. 4 shows an electron micrograph of the obtained solid solution, Fig. 6 (a) shows the result of powder X-ray diffraction, and Fig. 8 (a) shows an external view. For comparison, the result of powder X-ray diffraction of the waste asbestos of Reference Example 1 is shown in Fig. 6 (c).
[0062] 図 4及び図 6より、 廃アスベストはアルミン酸ナトリウムと混合すること により低温 (1 000°C) で固溶体となり、 針状結晶構造は消失して無害化 することがわかった。 また、 図 8より、 この固溶体は粉末状で得られること がわかった。 [0062] From Fig. 4 and Fig. 6, it was found that waste asbestos became a solid solution at a low temperature (1 000 ° C) when mixed with sodium aluminate, and the acicular crystal structure disappeared and became harmless. From Fig. 8, it was found that this solid solution was obtained in the form of powder.
[0063] [実施例 2] ケィ素■アルミニウム含有固溶体からのゼォライ 卜の調製 [0064] 実施例 1で得られた固溶体 5 gを 3. 5 N水酸化ナトリゥ厶溶液 1 00m [0063] [Example 2] Preparation of zeolite from solid solution containing aluminum ■ [0064] 5 g of the solid solution obtained in Example 1 was added to 3.5 N sodium hydroxide solution 100 m
Iに加え、 1 00°Cで 24時間加熱後、 水で数回洗浄し、 ろ紙でろ過後、 1 00°Cで乾燥して黄土色砂状の最終生成物 2. 3 g (ケィ素源に対する収率 46<½) を得た。 得られた最終生成物の電子顕微鏡写真を図 5に、 粉末 X線 回折の結果を図 6 (b) に、 粉末 X線回折による J CP DSカードチャート とのマッチングピークによる同定結果を図 7に、 及び外観写真を図 8 (b) にそれぞれ示した。 In addition to I, heated at 100 ° C for 24 hours, washed several times with water, filtered through filter paper, dried at 100 ° C, and finished with ocher-colored sandy final product 2.3 g The yield was 46 <½). Fig. 5 shows an electron micrograph of the final product obtained, Fig. 6 (b) shows the result of powder X-ray diffraction, and Fig. 7 shows the identification result based on the matching peak with the J CP DS card chart by powder X-ray diffraction. Figure 8 (b) shows the external appearance and, respectively.
[0065] 図 5及び図 6より、 廃アスベストとアルミン酸ナトリウムの固溶体をアル カリ処理することによリゼオラィ 卜の結晶が生成することがわかった。 また 、 図 7より、 生成したゼォライ トは主としてソーダライ トであることがわか つた。 さらに、 図 8より、 このゼォライ トは上記固溶体と同様に粉末状で得 られることがわかった。 [0065] From FIG. 5 and FIG. 6, it was found that a crystal of lysozyme koji was produced by treating the solid solution of waste asbestos and sodium aluminate with alkali. From Fig. 7, it was found that the generated zeolite was mainly sodalite. Furthermore, from FIG. 8, this zeolite can be obtained in the form of powder as in the case of the above solid solution. I found out that
[0066] [実施例 3] ゼォライ 卜の吸着能力の評価 [0066] [Example 3] Evaluation of adsorption capacity of zeorai
[0067] J I SK 1 474活性炭試験方法 5. 1. 2. 2 (メチレンブルー吸着性 能) に準じ、 ゼォライ 卜の吸着能力の評価試験を行った。 実施例 2で得られ た最終生成物、 ならびに比較のため錶物廃砂由来のゼォライ ト (ニチモウ製 ゼォキャスト) 及び石炭灰由来のゼォライ ト (九電産業製 C a型人工ゼオラ イ ト) を 0. 25 gずつそれぞれ共栓付容器に入れ、 メチレンブルー溶液 2 5 m I を加えて 30分振とう後ろ過した。 結果を図 9に示した。 [0067] In accordance with J I SK 1 474 activated carbon test method 5.1.2.2 (methylene blue adsorption capacity), an evaluation test of the adsorption capacity of Zeoli was performed. The final product obtained in Example 2 and, for comparison, zeolite derived from waste waste sand (Zeocast made by Nichimo) and zeolite derived from coal ash (Ca type artificial zeolite made by Kyuden Sangyo) Each 25 g was placed in a container with a stopper, and 25 mI of methylene blue solution was added and shaken for 30 minutes, followed by filtration. The results are shown in FIG.
[0068] 図 9より、 実施例 2で得られたゼォライ トは、 錶物廃砂由来ゼォライ ト及 び石炭灰由来ゼォライ 卜と同様の優れた吸着能を有することがわかった。 [0068] From Fig. 9, it was found that the zeolite obtained in Example 2 has the same excellent adsorbing ability as the waste waste-derived zeolite and the coal ash-derived zeolite.
[0069] [実施例 4] 各種加熱処理温度で調製したケィ素■アルミニウム含有固溶 体からのゼォライ 卜の調製 [0069] [Example 4] Preparation of zeolite from a solid solution containing aluminum prepared at various heat treatment temperatures
[0070] 加熱処理温度を 700°C、 800°C及び 900°Cとした以外は実施例 1 と 同様に処理して、 それぞれケィ素■アルミニウム固溶体 5. 8 g、 5. 7 g 及び 5. 6 gを得た。 得られた各固溶体の外観写真を図 1 0 (a) 、 図 1 1 (a) 及び図 1 2 (a) に、 また、 得られた固溶体の電子顕微鏡写真を図 1 3〜図 1 5にそれぞれ示した。 図 1 0〜図 1 2より、 これらの固溶体は粉末 状で得られ、 また、 図 1 3〜図 1 5より、 廃アスペストは 700~900°C の低温でも固溶体となり、 針状結晶構造は消失して無害化することがわかつ た。 なお、 加熱処理温度 700°Cでは、 わずかにアスベストの針状結晶構造 が認められるが、 ほとんど無害化していると考えられる。 [0070] The heat treatment was carried out in the same manner as in Example 1 except that the heat treatment temperatures were set to 700 ° C, 800 ° C, and 900 ° C, respectively. 6 g was obtained. Fig. 10 (a), Fig. 11 (a) and Fig. 12 (a) show the appearance photographs of the obtained solid solutions, and Fig. 13 to Fig. 15 show the electron micrographs of the obtained solid solutions. Shown respectively. From Fig. 10 to Fig. 12 these solid solutions are obtained in powder form, and from Fig. 13 to Fig. 15 the waste asbestos becomes a solid solution even at a low temperature of 700 to 900 ° C, and the acicular crystal structure disappears. I was able to make it harmless. At a heat treatment temperature of 700 ° C, a slight asbestos needle-like crystal structure is observed, but it is thought that it is almost harmless.
[0071] 上記でそれぞれ得られた固溶体 5. 5 gを用いた以外は実施例 2と同様に 処理して、 それぞれ最終生成物 3. 8 g、 3. 7 g及び 3. 6 gを得た。 得 られた最終生成物の電子顕微鏡写真を図 1 6〜図 1 8に、 粉末 X線回折の結 果を図 1 9 (a) 、 (b) 及び (c) に、 並びに外観写真を図 1 0 (b) 、 図 1 1 (b) 及び図 1 2 (b) にそれぞれ示した。 [0071] The same treatment as in Example 2 was carried out except that 5.5 g of the solid solution obtained above was used to obtain final products of 3.8 g, 3.7 g, and 3.6 g, respectively. . The electron micrographs of the final product obtained are shown in Figs. 16 to 18, the results of powder X-ray diffraction are shown in Figs. 19 (a), (b), and (c), and the appearance photo is shown in Fig. 1. This is shown in Fig. 1 (b), Fig. 1 1 (b) and Fig. 1 2 (b), respectively.
[0072] また、 固溶体の代わりに、 参考例 1の廃アスベストとアルミン酸ナトリゥ ムに水を加えてよく混合し、 水分を蒸発させて得られた混合物を用いた以外 は実施例 2と同様に処理して最終生成物を得た。 得られた最終生成物 (未加 熱) の電子顕微鏡写真を図 20に、 粉末 X線回折の結果を図 1 9 (d) に示 した。 なお、 比較のため、 実施例 2の最終生成物 (1 000°C) 及び参考例 1の廃アスベストの粉末 X線回折の結果を図 1 9 (e) 及び ( f ) にそれぞ れ示した。 [0072] Instead of the solid solution, water was added to the waste asbestos and sodium aluminate of Reference Example 1 and mixed well, and the mixture obtained by evaporating the water was used. Was treated in the same manner as in Example 2 to obtain the final product. The electron micrograph of the final product obtained (unheated) is shown in Fig. 20, and the results of powder X-ray diffraction are shown in Fig. 19 (d). For comparison, the powder X-ray diffraction results of the final product of Example 2 (1 000 ° C) and the waste asbestos of Reference Example 1 are shown in Figs. 19 (e) and (f), respectively. .
[0073] 図 1 6〜図 1 9より、 針状結晶構造は消失して完全に無害化しゼォライ ト が生成することがわかった。 また、 図 1 0〜図 1 2より、 これらのゼォライ トは上記の各固溶体と同様に粉末状で得られることがわかつた。 [0073] From FIG. 16 to FIG. 19, it was found that the acicular crystal structure disappeared and became completely harmless to produce zeolite. Also, from FIG. 10 to FIG. 12, it was found that these zeolites can be obtained in the form of powder as with the above solid solutions.
[0074] [実施例 5] 各種ケィ素■アルミニウム比率で調製したケィ素■アルミ二 ゥム含有固溶体からのゼォライ 卜の調製 [0074] [Example 5] Preparation of various types of zeolite ■ Clay prepared with aluminum ratio ■ Preparation of zeolite from solid solution containing aluminum
[0075] アルミン酸ナトリウムを 5. 0 g (廃アスベストとアルミン酸ナトリウム の重量比 2 : 1 ) 、 2. 5 g (廃アスベストとアルミン酸ナトリウムの重量 比 4 : 1 ) 及び 1. O g (廃アスベストとアルミン酸ナトリウムの重量比 1 0 : 1 ) とした以外は実施例 1 と同様に処理して、 それぞれケィ素■アルミ ニゥ厶固溶体 1 2. 5 g、 1 1. O g及び 1 0. 5 gを得た。 得られた固溶 体の電子顕微鏡写真を図 21〜図 23に、 粉末 X線回折の結果を図 24にそ れぞれ示した。 [0075] 5.0 g of sodium aluminate (weight ratio of waste asbestos to sodium aluminate 2: 1), 2.5 g (weight ratio of waste asbestos to sodium aluminate 4: 1) and 1. O g ( Treated as in Example 1 except that the weight ratio of waste asbestos to sodium aluminate was set to 10: 1). 5 g was obtained. Electron micrographs of the obtained solid solution are shown in Figs. 21 to 23, and the results of powder X-ray diffraction are shown in Fig. 24, respectively.
[0076] 上記でそれぞれ得られた固溶体 1 0 gを用いた以外は実施例 2と同様に処 理して、 それぞれ最終生成物 4. 57 g、 4. 1 1 g及び 3. 36 gを得た 。 得られた最終生成物の電子顕微鏡写真を図 25〜図 27にそれぞれ示した [0076] The same procedures as in Example 2 were performed except that 10 g of the solid solution obtained above was used, respectively, to obtain final products of 4.57 g, 4.11 g, and 3.36 g, respectively. The Electron micrographs of the final product obtained are shown in FIGS. 25 to 27, respectively.
[0077] 図 21〜図 24より、 固溶体では、 廃アスベストとアルミン酸ナトリウム の重量比 4 : 1〜 1 0 : 1 (ケィ素とアルミニウムのモル比 4 : 1〜 1 0 : 1 ) では、 アスベストの針状結晶構造が認められるが、 廃アスベストとアル ミン酸ナトリウムの重量比 2 : 1〜1 : 1 (ケィ素とアルミニウムのモル比 2 : 1〜1 : 1 ) では、 針状結晶構造は消失して完全に無害化することがわ かった。 [0077] From FIG. 21 to FIG. 24, in the solid solution, the weight ratio of waste asbestos to sodium aluminate is 4: 1 to 10: 1 (the molar ratio of silicon to aluminum is 4: 1 to 10: 1). In the weight ratio of waste asbestos to sodium aluminate 2: 1 to 1: 1 (the molar ratio of key to aluminum 2: 1 to 1: 1), the acicular crystal structure is It was found that it disappeared and became completely harmless.
[0078] また、 図 25〜図 27より、 最終生成物では、 廃アスベストとアルミン酸 ナトリウムの重量比 1 : 1 ~ 1 0 : 1 (ケィ素とアルミニウムのモル比 1 : 1 ~ 1 0 : 1 ) のすべてにおいてアスペス卜の針状結晶構造は認められず、 完全に無害化してゼォライ トが生成することがわかつた。 [0078] From Fig. 25 to Fig. 27, the final product is waste asbestos and aluminate. In all of the sodium weight ratios of 1: 1 to 10: 1 (the molar ratio of kaen to aluminum of 1: 1 to 10: 1), the needle-like crystal structure of Aspes was not observed, and it was completely detoxified. I was able to generate.
[0079] [実施例 6 ] 廃アスベストと水酸化アルミニウムからのケィ素■アルミ二 ゥム含有固溶体の調製 [0079] [Example 6] Preparation of silicon from waste asbestos and aluminum hydroxide ■ Preparation of solid solution containing aluminum
[0080] 水酸化アルミニウム 2 0 gと水酸化ナトリウム 1 O gを乳鉢の中でよくす りつぶし、 さらに参考例 1の廃アスベスト 3 0 gを加えてよく混合した。 得 られた混合物 2 0 gを無酸化雰囲気焼入炉で 1 0 0 0 °Cで 1時間加熱後冷却 して、 ケィ素■アルミニウム含有固溶体 1 7 gを得た。 得られた固溶体の電 子顕微鏡写真を図 2 8に示した。 また、 粉末 X線回折の結果を、 図 2 9に示 した。 [0080] 20 g of aluminum hydroxide and 1 O g of sodium hydroxide were well ground in a mortar, and 30 g of waste asbestos of Reference Example 1 was further added and mixed well. 20 g of the obtained mixture was heated at 100 ° C. for 1 hour in a non-oxidizing atmosphere quenching furnace and then cooled to obtain 17 g of a solid aluminum-containing solid solution. An electron micrograph of the obtained solid solution is shown in FIG. The results of powder X-ray diffraction are shown in Fig. 29.
[0081 ] 図 2 8及び図 2 9より、 得られた固溶体ではアスペス卜の針状結晶構造は 完全に消失しており、 アルミン酸ナトリウムの代わりに水酸化アルミニウム 及び水酸化ナトリゥ厶を用いても実施例 1 と同様の結果が得られることがわ かった。 [0081] From Fig. 28 and Fig. 29, in the obtained solid solution, the needle-like crystal structure of Aspes was completely lost, and even if aluminum hydroxide or sodium hydroxide was used instead of sodium aluminate, It was found that the same result as in Example 1 was obtained.
[0082] [実施例 7 ] 廃アスベストと廃アルミニウムからのケィ素■アルミニウム 含有固溶体の調製 [Example 7] Cyanide from waste asbestos and waste aluminum ■ Preparation of solid solution containing aluminum
[0083] 廃アルミニウム 3 gと水酸化ナトリウム 4 gを乳鉢の中でよくすりつぶし 、 さらに参考例 1の廃アスペストフ gを加えてよく混合した。 得られた混合 物 1 0 gを無酸化雰囲気焼入炉で 1 0 0 0 °Cで 1時間加熱後冷却して、 ケィ 素■アルミニウム含有固溶体 7 . 1 gを得た。 得られた固溶体の電子顕微鏡 写真を図 3 0に示した。 また、 粉末 X線回折の結果を、 図 3 1に示した。 [0083] 3 g of waste aluminum and 4 g of sodium hydroxide were thoroughly ground in a mortar, and the waste asbestos g of Reference Example 1 was further added and mixed well. The obtained mixture (10 g) was heated in a non-oxidizing atmosphere quenching furnace at 100 ° C. for 1 hour and then cooled to obtain 7.1 g of silicon / aluminum-containing solid solution. An electron micrograph of the obtained solid solution is shown in FIG. The results of powder X-ray diffraction are shown in Fig. 31.
[0084] 図 3 0及び図 3 1より、 得られた固溶体ではアスペス卜の針状結晶構造は 完全に消失しており、 アルミン酸ナトリウムの代わりに廃アルミニウム及び 水酸化ナトリゥムを用いても実施例 1 と同様の結果が得られることがわかつ た。 [0084] From FIG. 30 and FIG. 31, in the obtained solid solution, the needle-like crystal structure of Aspes was completely disappeared, and even when waste aluminum and sodium hydroxide were used instead of sodium aluminate, the examples were obtained. It was found that the same result as 1 was obtained.
[0085] [実施例 8 ] ケィ素■アルミニウム含有固溶体からの他の型のゼォライ ト の調製 [0086] アルミン酸ナトリウム 29 gを水 2 OOm Iに溶解してアルミン酸ナトリ ゥ厶溶液とした。 また、 水酸化ナトリウム 1 1 2 gを水 268 gに溶解し、 ケィ酸ナトリウム 420 gを加えてケィ酸ナトリウム溶液とした。 得られた アルミン酸ナトリウム溶液とケィ酸ナトリウム溶液を混合して、 1 5°Cで 1 6時間熟成しスラリーとした。 [0085] [Example 8] Preparation of other types of zeolite from solid solution containing aluminum [0086] 29 g of sodium aluminate was dissolved in 2 OOm I of water to obtain a sodium aluminate solution. Further, 112 g of sodium hydroxide was dissolved in 268 g of water, and 420 g of sodium silicate was added to obtain a sodium silicate solution. The obtained sodium aluminate solution and sodium silicate solution were mixed and aged at 15 ° C. for 16 hours to form a slurry.
[0087] ケィ酸ナトリウム 34 gと水酸化ナトリウム 1 2. 3 gを水 1 1 2. 2 g に溶解してケィ酸ナトリウム溶液とした。 得られたケィ酸ナトリウム溶液 1 0. 6 gに実施例 1 と同様にして得られたケィ素■アルミニウム含有固溶体 3. 3 gを混合して 24時間熟成し、 1 00°Cに加熱し、 ケィ酸 35 g、 水 酸化ナトリウム 2 g、 水 35 g及びスラリー 4m I を加えて 1 05°Cで 36 時間加熱した後、 ろ過乾燥して、 黄土色砂状の最終生成物を得た。 得られた 最終生成物の電子顕微鏡写真を図 32に、 粉末 X線回折の結果を図 33に、 及び粉末 X線回折による J C P D Sカードチャートとのマッチングピークに よる同定結果を図 34にそれぞれ示した。 [0087] 34 g of sodium silicate and 12.3 g of sodium hydroxide were dissolved in 1 12.2 g of water to obtain a sodium silicate solution. The sodium kainate solution 10.6 g obtained was mixed in the same manner as in Example 1 with the silicon-aluminum-containing solid solution 3.3 g, aged for 24 hours, heated to 100 ° C, 35 g of caic acid, 2 g of sodium hydroxide, 35 g of water and 4 ml of slurry were added and heated at 105 ° C. for 36 hours, followed by filtration and drying to obtain an ocher sandy final product. Fig. 32 shows the electron micrograph of the final product obtained, Fig. 33 shows the result of powder X-ray diffraction, and Fig. 34 shows the result of identification by the matching peak with the JCPDS card chart by powder X-ray diffraction. .
[0088] 図 32及び図 33より、 アスペス卜の針状結晶構造は消失して無害化しゼ オライ トの結晶が生成することがわかった。 また、 図 34より、 生成したゼ ォライ トは主としてソーダライ 卜とゼォライ ト Pの混合型であることがわか つた。 [0088] From FIG. 32 and FIG. 33, it was found that the needle-like crystal structure of Aspes was disappeared and detoxified to produce zeolite crystals. Also, from Fig. 34, it was found that the generated zeolite was mainly a mixed type of soda rai and zeolite Z.
[0089] [実施例 9] ケィ素■アルミニウム含有固溶体からの他の型のゼォライ ト の調製 [0089] [Example 9] Preparation of other types of zeolite from solid solution containing aluminum
[0090] アルミン酸ナトリウム 29 gを水 2 OOm Iに溶解してアルミン酸ナトリ ゥム溶液とした。 また、 水酸化ナトリウム 1 1 2 gを水 268 gに溶解し、 ケィ酸ナトリウム 420 gを加えてケィ酸ナトリウム溶液とした。 得られた アルミン酸ナトリウム溶液とケィ酸ナトリウム溶液を混合して、 1 5°Cで 1 6時間熟成しスラリーとした。 実施例 1 と同様にして得られたケィ素■アル ミニゥム含有固溶体 4. 5 gとアスベストの溶融スラグ 3. 3 gをよく混合 し、 さらにケィ素■アルミニウム含有固溶体 4. 69 g、 水 47m l及びス ラリー 2 m l を加え、 1. 5 a t mの加圧下 1 00°Cで 40時間加熱した後 ろ過し、 1~1カ《1 0以下になるまで洗浄後 1 05°〇で1 6時間乾燥して、 黄 土色砂状の最終生成物 9. 6 gを得た。 得られた最終生成物の電子顕微鏡写 真を図 35に、 粉末 X線回折の結果を図 36に、 及び粉末 X線回折による J C P DSカードチャートとのマッチングピークによる同定結果を図 37にそ れぞれ示した。 [0090] 29 g of sodium aluminate was dissolved in 2 OOm I of water to obtain a sodium aluminate solution. Further, 112 g of sodium hydroxide was dissolved in 268 g of water, and 420 g of sodium silicate was added to obtain a sodium silicate solution. The obtained sodium aluminate solution and sodium silicate solution were mixed and aged at 15 ° C. for 16 hours to form a slurry. Obtained in the same manner as in Example 1 ■ Algium-containing solid solution 4.5 g and asbestos molten slag 3.3 g were mixed well, and then Key ■ Aluminum-containing solid solution 4.69 g, water 47 ml After adding 2 ml of slurry and heating at 100 ° C for 40 hours under 1.5 atm pressure After filtration, washing to 1 to 1 << 10 or less, and drying at 105 °° for 16 hours, 9.6 g of an ocher sandy final product was obtained. The electron micrograph of the final product obtained is shown in Fig. 35, the result of powder X-ray diffraction is shown in Fig. 36, and the result of identification by matching peak with JCP DS card chart by powder X-ray diffraction is shown in Fig. 37. I showed them.
[0091] 図 35及び図 36より、 アスペス卜の針状結晶構造は消失して無害化しゼ オライ トの結晶が生成することがわかった。 また、 図 37より、 生成したゼ ォライ トは主としてソーダライ 卜とゼォライ ト Aの混合型であることがわか つた。 [0091] From FIG. 35 and FIG. 36, it was found that the needle-like crystal structure of Aspes was lost and made harmless, and a zeolite crystal was formed. In addition, from Fig. 37, it was found that the generated zeolite was mainly a mixed type of soda light and zeolite A.
[0092] [実施例 1 0] マイクロウエーブ照射によるゼォライ 卜の調製 [0092] [Example 10] Preparation of zeoli candy by microwave irradiation
[0093] 参考例 1の廃アスペスト 1 00 gとアルミン酸ナトリウム 1 00 gに水 2 50m I を加えてよく混合し、 水分を蒸発させて廃アスペス卜とアルミン酸 ナトリゥ厶の混合物とした。 得られた混合物 1. 0 gに同量のカーボンと水 を添加し、 家庭用電子レンジ (岩谷産業製 I M575型、 AC 1 00V、 定 格消費電力 900W、 定格高周波出力 50 OW) に入れマイクロウエーブを 1 0分間照射して、 ケィ素■アルミニウム含有固溶体 0. 78 gを得た。 得 られた固溶体の電子顕微鏡写真を図 38に示した。 これより、 わずかにァス べス卜の針状結晶構造が認められるが、 ほとんど無害化していることが推察 される。 [0093] To 250 g of waste aspest of Reference Example 1 and 100 g of sodium aluminate, 250 mI of water was added and mixed well, and the water was evaporated to obtain a mixture of waste asbestos and sodium aluminate. Add the same amount of carbon and water to 1.0 g of the resulting mixture, and put it in a microwave oven (Iwatani Sangyo I M575, AC 100 V, rated power consumption 900 W, rated high-frequency output 50 OW). The wave was irradiated for 10 minutes to obtain 0.78 g of solid aluminum-containing solid solution. An electron micrograph of the obtained solid solution is shown in FIG. From this, a slightly needle-like crystal structure of Asbestos is recognized, but it is presumed that it is almost harmless.
[0094] 上記で得られた固溶体を用いた以外は実施例 2と同様に処理して、 最終生 成物 0. 42 gを得た。 得られた最終生成物の電子顕微鏡写真を図 39に、 粉末 X線回折の結果を図 40 (a) にそれぞれ示した。 なお、 比較のため、 実施例 2の最終生成物 (無酸化雰囲気焼入炉で加熱処理) の粉末 X線回折の 結果を図 40 (b) に示した。 [0094] The same treatment as in Example 2 was carried out except that the solid solution obtained above was used to obtain 0.42 g of the final product. The electron micrograph of the final product obtained is shown in Fig. 39, and the results of powder X-ray diffraction are shown in Fig. 40 (a). For comparison, the result of powder X-ray diffraction of the final product of Example 2 (heat treatment in a non-oxidizing atmosphere quenching furnace) is shown in FIG. 40 (b).
[0095] 図 39及び図 40より、 得られた最終生成物では、 針状結晶構造が完全に 消失してォライ 卜が生成しており、 マイクロウエーブ照射による加熱処理に よって極めて短時間で実施例 2と同様のゼォライ トを製造できることがわか つた。 [0096] [実施例 1 1 ] ケィ素含有固溶体からのゼォライ 卜の調製 [0095] From FIG. 39 and FIG. 40, in the obtained final product, the needle-like crystal structure disappeared completely, and soot was formed, and the embodiment was carried out in a very short time by heat treatment by microwave irradiation. It was found that the same zeolite as 2 can be produced. [0096] [Example 1 1] Preparation of zeoli soot from a solid solution containing silicon
[0097] アルミン酸ナトリウムの代わりにケィ酸ナトリウム (ケィ酸ナトリウム 5 g、 廃アスベスト 5 g) を用いた以外は実施例 1 と同様に処理して、 ケィ素 固溶体 7. 4 gを得た。 得られた固溶体の電子顕微鏡写真を図 41に示した 。 これより、 アスベストの針状結晶構造は消失し、 無害化していることがわ かった。 [0097] Treatment was performed in the same manner as in Example 1 except that sodium silicate (5 g of sodium silicate, 5 g of waste asbestos) was used instead of sodium aluminate to obtain 7.4 g of potassium solid solution. An electron micrograph of the obtained solid solution is shown in FIG. As a result, it was found that the needle-like crystal structure of asbestos disappeared and became harmless.
[0098] 得られた固溶体 0. 5 gとアルミン酸ナトリウム 0. 25 gを混合し、 3 . 5 N水酸化ナトリゥム溶液 1 00m lに加え、 1 00°Cで 24時間加熱後 水で数回洗浄し、 ろ紙でろ過後 1 oo°cで乾燥して、 黄土色砂状の最終生成 物 0. 49 gを得た。 得られた最終生成物の電子顕微鏡写真を図 42に、 粉 末 X線回折の結果を図 43 (a) にそれぞれ示した。 なお、 比較のため、 実 施例 2の最終生成物 (ケィ素■アルミニウム含有固溶体からの調整) の粉末 X線回折の結果を図 43 (b) に示した。 [0098] 0.5 g of the obtained solid solution and 0.25 g of sodium aluminate were mixed, added to 100 ml of 3.5 N sodium hydroxide solution, heated at 100 ° C for 24 hours, and then several times with water. It was washed, filtered through filter paper, and dried at 1 oo ° C to obtain 0.49 g of an ocher sandy final product. The electron micrograph of the final product obtained is shown in Fig. 42, and the results of powder X-ray diffraction are shown in Fig. 43 (a). For comparison, the result of powder X-ray diffraction of the final product of Example 2 (preparation from a silicon / aluminum-containing solid solution) is shown in FIG. 43 (b).
[0099] 図 42及び図 43より、 得られた最終生成物では、 針状結晶構造が完全に 消失してォライ 卜が生成しており、 ケィ素含有固溶体からも実施例 2と同様 のゼォライ トを製造できることがわかった。 [0099] From FIG. 42 and FIG. 43, in the final product obtained, the needle-like crystal structure disappeared completely, and soot crystals were formed, and the same zeolite as in Example 2 was also obtained from the silicon-containing solid solution. It was found that can be manufactured.
[0100] [参考例 2] 廃アスベストの溶融スラグの調製 [0100] [Example 2] Preparation of molten slag from waste asbestos
[0101] 参考例 1の廃アスペスト 40 gを、 高温電気炉で平均 1 500°Cで 4時間 加熱溶融した後室温まで冷却し、 廃アスベストの溶融スラグ 26. O gを得 た。 得られた溶融スラグの電子顕微鏡写真を図 44に、 粉末 X線回折の結果 を図 46 (a) にそれぞれ示した。 なお、 比較のため、 参考例 1の廃ァスべ ストの粉末 X線回折の結果を図 46 (c) に示した。 [0101] 40 g of the waste asbestos of Reference Example 1 was heated and melted in a high-temperature electric furnace at an average temperature of 1 500 ° C for 4 hours and then cooled to room temperature to obtain 26.Og of molten asbestos molten slag. Fig. 44 shows an electron micrograph of the molten slag obtained, and Fig. 46 (a) shows the results of powder X-ray diffraction. For comparison, Fig. 46 (c) shows the results of powder X-ray diffraction of the waste gas best in Reference Example 1.
[0102] 図 44及び図 46より、 廃アスベストは加熱することにより塊状の溶融ス ラグとなり、 針状結晶構造は消失して無害化することがわかった。 [0102] From Fig. 44 and Fig. 46, it was found that waste asbestos became a massive molten slag by heating, and the acicular crystal structure disappeared and became harmless.
[0103] [実施例 1 2] 廃アスベストの溶融スラグ及びアルミン酸ナトリウムから のゼォライ 卜の調製 [0103] [Example 1 2] Preparation of zeoli cake from waste asbestos molten slag and sodium aluminate
[0104] 参考例 2で得られた溶融スラグ 1 0 g及びアルミン酸ナトリウム 1 O gを [0104] The molten slag 10 g obtained in Reference Example 2 and sodium aluminate 1 O g were used.
3. 5 N水酸化ナトリゥム溶液 1 60m lに加え、 1 00°Cで 24時間加熱 後水で数回洗浄し、 遠心分離機で分離後 1 oo°cで乾燥して、 黄土色砂状の 最終生成物 1 3. 9 g (ケィ素源に対する収率 1 39%) を得た。 得られた 最終生成物の電子顕微鏡写真を図 45に、 粉末 X線回折の結果を図 46 (b ) にそれぞれ示した。 3. Add 5N sodium hydroxide solution to 60ml and heat at 100 ° C for 24 hours After washing with water several times, separating with a centrifuge and drying at 1 oo ° C to obtain 13.9 g of ocher sandy final product (yield to key source 1 39%) . FIG. 45 shows an electron micrograph of the final product obtained, and FIG. 46 (b) shows the result of powder X-ray diffraction.
[0105] 図 45及び図 46より、 廃アスベストの溶融スラグとアルミン酸ナトリウ ムをアルカリ処理することによリゼオライ トの結晶が生成することがわかつ た。 [0105] From Fig. 45 and Fig. 46, it was found that lysoleite crystals were produced by alkali treatment of molten asbestos molten slag and sodium aluminate.
[0106] [比較例 1 ] 廃アスペスト及びアルミン酸ナトリゥムからのゼォライ 卜の 調製 [0106] [Comparative Example 1] Preparation of zeoli cake from waste aspest and sodium aluminate
[0107] 溶融スラグの代わりに廃アスペスト 1 0 gを用いた以外は実施例 1 2と同 様に処理して、 黄土色針状繊維状の最終生成物 7. 7 g (ケィ素源に対する 収率 76. 9%) を得た。 得られた最終生成物の電子顕微鏡写真を図 47に 示した。 [0107] The same processing as in Example 1 2 except that 10 g of waste asbestos was used instead of molten slag was carried out to obtain 7.7 g of oval needle-like fibrous final product (concentration on the key source). The rate was 76.9%). An electron micrograph of the final product obtained is shown in FIG.
[0108] 図 47より、 廃アスベストとアルミン酸ナトリウムをアルカリ処理しても 、 針状の結晶構造が残存し無害化しておらず、 ゼォライ トも生成しないこと がわかった。 [0108] From FIG. 47, it was found that even when waste asbestos and sodium aluminate were treated with alkali, a needle-like crystal structure remained and was not detoxified, and no zeolite was produced.
[0109] [比較例 2] 廃アスベストの溶融スラグからのゼォライ トの調製 [0109] [Comparative Example 2] Preparation of zeolite from molten asbestos molten slag
[0110] 溶融スラグ及びアルミン酸ナトリウムの代わりに溶融スラグ 20 gを用い た以外は実施例 1 2と同様に処理して、 灰色粒状の最終生成物 1 0. 4 g ( ケィ素源に対する収率 1 04. 2<½) を得た。 得られた最終生成物の電子顕 微鏡写真を図 48に示した。 [0110] The same treatment as in Example 12 was conducted except that 20 g of molten slag was used instead of molten slag and sodium aluminate. 1 04. 2 <½) was obtained. An electron micrograph of the final product obtained is shown in FIG.
[0111] 図 48より、 溶融スラグにアルミン酸ナトリウムを加えずにアルカリ処理 しても、 廃アスベストの形状はアモルファス状のまま変化せず、 ゼォライ ト が生成しないことがわかつた。 [0111] From Fig. 48, it was found that even when the molten slag was alkali-treated without adding sodium aluminate, the shape of the waste asbestos remained amorphous and no zeolite was formed.
[0112] [実施例 1 3] 廃アスベストの溶融スラグ及び廃アルミニウムからのゼォ ライ 卜の調製 [0112] [Example 1 3] Preparation of zeolite slag from molten asbestos slag and waste aluminum
[0113] アルミン酸ナトリゥムの代わりに市販の清涼飲料水の蓋から採取した廃ァ ルミ二ゥムを用いた以外は実施例 1 と同様に処理して、 黄土色砂状の最終生 成物 1 7. 6 g (ケィ素源に対する収率 1 76. 7%) を得た。 得られた最 終生成物の電子顕微鏡写真を図 49に示した。 [0113] In the same manner as in Example 1 except that waste aluminum collected from the lid of a commercial soft drink is used instead of sodium aluminate, the ocher-colored sandy final product is obtained. 17.6 g of the product (yield 1 76.7% based on the key source) was obtained. An electron micrograph of the final product obtained is shown in FIG.
[0114] 図 49より、 アルミニウム源として廃アルミを用いた場合も、 実施例 1 2 とほぼ同様の結果が得られることがわかつた。 [0114] From Fig. 49, it was found that the same results as in Example 1 2 were obtained when waste aluminum was used as the aluminum source.
[0115] [実施例 1 4] 無害化廃アスベスト溶融物と溶融点降下物質との熱処理後 の外観評価 [0115] [Example 14] Appearance evaluation after heat treatment of detoxified waste asbestos melt and melting point depressant
[0116] 廃棄物の処理及び清掃に関する法律 (廃棄物処理法) 等の改正により、 一 般的な事業所等の設備ではアスペス卜の取り扱いが困難になったため、 本発 明においては、 参考例 1の廃アスペストを 1 500°Cで加熱処理し、 無害化 した岩石状の廃アスペスト溶融物を粉状に粉砕したものを用いて実験を行つ た。 なお、 無害化した岩石状の廃アスベスト溶融物の外観写真を図 50 (a ) に、 これを粉状に粉砕したものの外観写真を図 50 (b) に示した。 [0116] Due to the revision of the Waste Disposal and Cleaning Law (Waste Treatment Law), etc., it became difficult to handle Aspes-Sardine at facilities in general offices. An experiment was conducted using 1 waste asbestos heat-treated at 1500 ° C and detoxified rock-like waste asbestos melt. Fig. 50 (a) shows an external view of the detoxified rock-like waste asbestos melt, and Fig. 50 (b) shows an external view of the crushed powder.
[0117] アルミン酸ナトリウムと前記無害化廃アスペスト溶融物粉末とを重量比 1 [0117] Sodium aluminate and detoxified waste aspaste melt powder in weight ratio 1
: 1で混合し、 卓上小型電気炉を用いて 800°C及び 1 200°Cで熱処理を 行った。 得られた生成物の外観写真を図 51及び図 52にそれぞれ示した。 図 51より、 800°Cで熱処理を行った生成物の外観は粉末状であり、 図 5 2より、 1 200°Cで熱処理を行った生成物の外観は塊状であることがわか つた。 : Mixed at 1, and heat-treated at 800 ° C and 1 200 ° C using a small desktop electric furnace. The appearance photographs of the obtained product are shown in FIGS. 51 and 52, respectively. From FIG. 51, it was found that the appearance of the product heat-treated at 800 ° C. was powdery, and from FIG. 52, the appearance of the product heat-treated at 1 200 ° C. was massive.
[0118] また、 ケィ酸カルシウム又はケィ酸カルシウムに酸化アルミニウムを 1 5 %混合したものと、 無害化廃アスベスト溶融物粉末とを重量比 1 : 1で混合 し、 卓上小型電気炉を用いて 1 200°Cで加熱処理を行った。 得られた生成 物の外観写真を図 53及び図 54にそれぞれ示した。 また、 無害化廃ァスべ スト溶融物粉末に酸化アルミニウムを 1 5%混合し、 上記と同様の条件で加 熱処理を行った。 得られた各生成物の外観写真を図 55に示した。 図 53〜 図 55より、 1 200°Cで熱処理を行った各生成物の外観は塊状であること がわかった。 [0118] In addition, calcium silicate or calcium silicate mixed with 15% aluminum oxide and detoxified waste asbestos melt powder were mixed at a weight ratio of 1: 1, and then a tabletop small electric furnace was used. Heat treatment was performed at 200 ° C. The appearance photographs of the obtained product are shown in FIGS. 53 and 54, respectively. Further, 15% of aluminum oxide was mixed with the harmless waste gas best melt powder, and heat treatment was performed under the same conditions as described above. An appearance photograph of each product obtained is shown in FIG. From Fig. 53 to Fig. 55, it was found that the appearance of each product heat-treated at 1 200 ° C was agglomerated.
[0119] 実施例 1、 4及び 1 4の結果より、 本発明のゼォライ 卜の製造工程におけ る最適な熱処理温度は、 熱処理後の生成物の外観が粉末状である 1 000°C 以下であることがわかつた。 [0119] From the results of Examples 1, 4 and 14, the optimum heat treatment temperature in the production process of the zeolite cake of the present invention is that the appearance of the product after the heat treatment is 1 000 ° C. I found out that:
産業上の利用可能性 Industrial applicability
[0120] 本発明のゼォライ 卜の製造方法によれば、 従来法に比べて極めて低温で廃 アスペストを含む原料混合物を溶融固溶化し、 アスペス卜の針状結晶構造を 消失させ無害化することができるので、 経済的負担をかけることなく、 それ を有効に再利用して簡易にゼォライ トを製造することができる。 また、 その 生成物が粉末状であるので、 取り扱いが容易で運搬性に優れた原材料を用い てゼオライ トを製造することができる。 さらに、 廃アスベストを含む原料混 合物中に有害ガスの発生源となり得る物質を含まないので、 安全性に優れた 原材料を用いてゼォライ トを製造することができる。 [0120] According to the method for producing Zeoli rice cake of the present invention, the raw material mixture containing waste Aspest is melted and dissolved at an extremely low temperature as compared with the conventional method, and the needle-like crystal structure of Asbestos rice cake is eliminated and rendered harmless. As a result, it is possible to manufacture zeolite easily by effectively reusing it without imposing an economic burden. In addition, since the product is in powder form, zeolite can be produced using raw materials that are easy to handle and have excellent transportability. Furthermore, since the raw material mixture containing waste asbestos does not contain substances that can be a source of harmful gases, zeolite can be manufactured using raw materials with excellent safety.
[0121 ] 従って、 本発明のゼォライ 卜の製造方法により得られるゼォライ トは極め てすぐれた吸着能を有し、 シックハウス症候群の原因とされるホルムアルデ ヒド等の吸着能力、 調湿能力や吸湿能力を利用した建材への応用、 美術館へ の応用、 有害物質の吸着能力を利用した土壌改善剤への応用、 環境ホルモン の吸着、 汚水処理や浄水場での利用、 におい、 アンモニアの吸着能力を利用 したペット用、 車、 家庭用消臭剤等として利用した場合、 極めて有用である 図面の簡単な説明 [0121] Therefore, the zeolite obtained by the method for producing the zeolite cake of the present invention has an extremely excellent adsorption ability, and has the ability to adsorb formaldehyde and the like, which are the cause of sick house syndrome, and the moisture conditioning ability and moisture absorption ability. Application to building materials used, application to museums, application to soil improvers using the adsorption capacity of harmful substances, adsorption of environmental hormones, use in sewage treatment and water treatment plants, smell, and adsorption capacity of ammonia It is extremely useful when used as a deodorant for pets, cars, households, etc. Brief Description of Drawings
[0122] [図 1 ]使用した廃アスベストの光学顕微鏡 (落射簡易偏光) 写真である (参考 例 1 ) 。 [0122] [Fig. 1] Photo of the used asbestos optical microscope (simple incident polarized light) (Reference Example 1).
[図 2]使用した廃アスベストの電子顕微鏡写真である (参考例 1 ) 。 [Fig. 2] An electron micrograph of the used asbestos (Reference Example 1).
[図 3]使用した廃アスペス卜の粉末 X線回折による J C P D Sカードチャート とのマッチングピークによる同定結果である (参考例 1 ) 。 [Fig. 3] The result of identification by matching peak with the JCPDS card chart by powder X-ray diffraction of the waste asbestos used (Reference Example 1).
[図 4]廃アスペス卜とアルミン酸ナトリウムから得られたケィ素■アルミニゥ ム含有固溶体の電子顕微鏡写真である (実施例 1 ) 。 FIG. 4 is an electron micrograph of a solid aluminum-containing solid solution obtained from waste asbestos and sodium aluminate (Example 1).
[図 5]実施例 1のケィ素■アルミニウム含有固溶体から得られた最終生成物の 電子顕微鏡写真である (実施例 2 ) 。 FIG. 5 is an electron micrograph of the final product obtained from the solid aluminum-containing solid solution of Example 1 (Example 2).
[図 6]実施例 1の固溶体、 実施例 2の最終生成物及び参考例 1の廃アスペスト の粉末 X線回折の結果である。 [Fig. 6] Solid solution of Example 1, final product of Example 2, and waste asbestos of Reference Example 1. It is the result of powder X-ray diffraction.
[図 7]実施例 2の最終生成物の粉末 X線回折による J CPDSカードチャート とのマッチングピークによる同定結果である。 FIG. 7 is an identification result by a matching peak with a J CPDS card chart by powder X-ray diffraction of the final product of Example 2.
[図 8]実施例 1のケィ素■アルミニウム含有固溶体、 及び実施例 2の最終生成 物の外観写真である。 FIG. 8 is an appearance photograph of the silicon / aluminum-containing solid solution of Example 1 and the final product of Example 2.
[図 9]実施例 2の最終生成物の吸着能力の評価試験結果である (実施例 3) 。 FIG. 9 shows the results of an evaluation test of the adsorption capacity of the final product of Example 2 (Example 3).
[図 10]加熱処理温度 700°Cで得られたケィ素■アルミニウム含有固溶体 ( 実施例 4) 、 及びその最終生成物の外観写真である。 FIG. 10 is an appearance photograph of a silicon / aluminum-containing solid solution obtained at a heat treatment temperature of 700 ° C. (Example 4) and its final product.
[図 11]加熱処理温度 800°Cで得られたケィ素■アルミニウム含有固溶体 ( 実施例 4) 、 及びその最終生成物の外観の写真である。 FIG. 11 is a photograph of the appearance of a silicon / aluminum-containing solid solution (Example 4) obtained at a heat treatment temperature of 800 ° C. and its final product.
[図 12]加熱処理温度 900°Cで得られたケィ素■アルミニウム含有固溶体 ( 実施例 4) 、 及びその最終生成物の外観写真である。 FIG. 12 is an appearance photograph of a silicon / aluminum-containing solid solution obtained at a heat treatment temperature of 900 ° C. (Example 4) and its final product.
[図 13]加熱処理温度 700°Cで得られたケィ素■アルミニウム固溶体の電子 顕微鏡写真である (実施例 4) 。 FIG. 13 is an electron micrograph of a silicon / aluminum solid solution obtained at a heat treatment temperature of 700 ° C. (Example 4).
[図 14]加熱処理温度 800°Cで得られたケィ素■アルミニウム固溶体の電子 顕微鏡写真である (実施例 4) 。 FIG. 14 is an electron micrograph of a silicon / aluminum solid solution obtained at a heat treatment temperature of 800 ° C. (Example 4).
[図 15]加熱処理温度 900°Cで得られたケィ素■アルミニウム固溶体の電子 顕微鏡写真である (実施例 4) 。 FIG. 15 is an electron micrograph of a silicon / aluminum solid solution obtained at a heat treatment temperature of 900 ° C. (Example 4).
[図 16]加熱処理温度 700°Cで得られた最終生成物の電子顕微鏡写真である (実施例 4) 。 FIG. 16 is an electron micrograph of the final product obtained at a heat treatment temperature of 700 ° C. (Example 4).
[図 17]加熱処理温度 800°Cで得られた最終生成物の電子顕微鏡写真である (実施例 4) 。 FIG. 17 is an electron micrograph of the final product obtained at a heat treatment temperature of 800 ° C. (Example 4).
[図 18]加熱処理温度 900°Cで得られた最終生成物の電子顕微鏡写真である (実施例 4) 。 FIG. 18 is an electron micrograph of the final product obtained at a heat treatment temperature of 900 ° C. (Example 4).
[図 19]加熱処理温度 700°C、 800°C、 900°C、 未加熱 (実施例 4) 及 び 1 000°C (実施例 2) で得られた最終生成物ならびに廃アスベスト (参 考例 1 ) の粉末 X線回折の結果である。 [Figure 19] Heat treatment temperatures 700 ° C, 800 ° C, 900 ° C, unheated (Example 4) and 1 000 ° C (Example 2) final product and waste asbestos (reference) It is the result of powder X-ray diffraction of Example 1).
[図 20]未加熱で得られた最終生成物の電子顕微鏡写真である (実施例 4) 。 [図 21 ]廃アスベストとアルミン酸ナトリウムの重量比 2 : 1で得られた固溶 体の電子顕微鏡写真である (実施例 5 ) 。 FIG. 20 is an electron micrograph of the final product obtained without heating (Example 4). FIG. 21 is an electron micrograph of a solid solution obtained with a weight ratio of waste asbestos to sodium aluminate of 2: 1 (Example 5).
[図 22]廃アスベストとアルミン酸ナトリウムの重量比 4 : 1で得られた固溶 体の電子顕微鏡写真である (実施例 5 ) 。 FIG. 22 is an electron micrograph of a solid solution obtained at a weight ratio of waste asbestos to sodium aluminate of 4: 1 (Example 5).
[図 23]廃アスベストとアルミン酸ナトリウムの重量比 1 0 : 1で得られた固 溶体の電子顕微鏡写真である (実施例 5 ) 。 FIG. 23 is an electron micrograph of a solid solution obtained with a weight ratio of waste asbestos to sodium aluminate of 10: 1 (Example 5).
[図 24]廃アスベストとアルミン酸ナトリウムの重量比 2 : 1 , 4 : 1及び 1 0 : 1で得られた固溶体の粉末 X線回折の結果である (実施例 5 ) 。 FIG. 24 is a result of powder X-ray diffraction of a solid solution obtained at a weight ratio of waste asbestos to sodium aluminate of 2: 1, 4: 1 and 10: 1 (Example 5).
[図 25]廃アスベストとアルミン酸ナトリウムの重量比 2 : 1で得られた最終 生成物の電子顕微鏡写真である (実施例 5 ) 。 FIG. 25 is an electron micrograph of the final product obtained with a weight ratio of waste asbestos to sodium aluminate of 2: 1 (Example 5).
[図 26]廃アスベストとアルミン酸ナトリウムの重量比 4 : 1で得られた最終 生成物の電子顕微鏡写真である (実施例 5 ) 。 FIG. 26 is an electron micrograph of the final product obtained at a weight ratio of waste asbestos to sodium aluminate of 4: 1 (Example 5).
[図 27]廃アスベストとアルミン酸ナトリウムの重量比 1 0 : 1で得られた最 終生成物の電子顕微鏡写真である (実施例 5 ) 。 FIG. 27 is an electron micrograph of the final product obtained with a weight ratio of waste asbestos to sodium aluminate of 10: 1 (Example 5).
[図 28]廃アスペス卜と水酸化アルミニウムから得られたケィ素■アルミニゥ ム含有固溶体の電子顕微鏡写真である (実施例 6 ) 。 FIG. 28 is an electron micrograph of a solid aluminum-containing solid solution obtained from waste asbestos and aluminum hydroxide (Example 6).
[図 29]廃アスペス卜と水酸化アルミニウムから得られたケィ素■アルミニゥ 厶含有固溶体の粉末 X線回折の結果である。 FIG. 29 is a result of powder X-ray diffraction of a solid solution containing silicon / aluminum soot obtained from waste asbestos and aluminum hydroxide.
[図 30]廃アスペス卜と廃アルミニウムから得られたケィ素■アルミニウム含 有固溶体の電子顕微鏡写真である (実施例 7 ) 。 FIG. 30 is an electron micrograph of a solid aluminum-containing solid solution obtained from waste asbestos and waste aluminum (Example 7).
[図 31 ]廃アスペス卜と廃アルミニウムから得られたケィ素■アルミニウム含 有固溶体の粉末 X線回折の結果である。 [Fig. 31] Results of powder X-ray diffraction of solid aluminum-containing solid solution obtained from waste aspaste and waste aluminum.
[図 32]ケィ素■アルミニウム含有固溶体から得られた他の型の最終生成物の 電子顕微鏡写真である (実施例 8 ) 。 FIG. 32 is an electron micrograph of another type of final product obtained from the solid aluminum-containing solid solution (Example 8).
[図 33]実施例 8の最終生成物の粉末 X線回折の結果である。 FIG. 33 shows the result of powder X-ray diffraction of the final product of Example 8.
[図 34]実施例 8の最終生成物の粉末 X線回折による J C P D Sカードチヤ一 卜とのマッチングピークによる同定結果である。 FIG. 34 shows the result of identification of the final product of Example 8 by a matching peak with a powdery X-ray diffraction pattern of a JC PDS card.
[図 35]ケィ素■アルミニウム含有固溶体から得られた他の型の最終生成物の 電子顕微鏡写真である (実施例 9 ) 。 [Fig.35] Key types of other types of final products obtained from aluminum-containing solid solutions It is an electron micrograph (Example 9).
[図 36]実施例 9の最終生成物の粉末 X線回折の結果である。 FIG. 36 is the result of powder X-ray diffraction of the final product of Example 9.
[図 37]実施例 9の最終生成物の粉末 X線回折による J C P D Sカードチヤ一 卜とのマッチングピークによる同定結果である。 FIG. 37 shows the result of identification of the final product of Example 9 by a matching peak with a powdery X-ray diffraction pattern of a JCPDS card.
[図 38]マイクロウエーブ照射による加熱処理によって得られたケィ素■アル ミニゥム固溶体の電子顕微鏡写真である (実施例 1 0 ) 。 FIG. 38 is an electron micrograph of a carbon solid aluminum solution obtained by heat treatment by microwave irradiation (Example 10).
[図 39]マイク口ウェーブ照射による加熱処理によつて得られた最終生成物の 電子顕微鏡写真である (実施例 1 0 ) 。 FIG. 39 is an electron micrograph of the final product obtained by heat treatment using microwave irradiation (Example 10).
[図 40]実施例 1 0及び実施例 2の最終生成物の粉末 X線回折の結果である。 FIG. 40 is a result of powder X-ray diffraction of the final product of Example 10 and Example 2.
[図 41 ]ケィ素含有固溶体の電子顕微鏡写真である (実施例 1 1 ) 。 FIG. 41 is an electron micrograph of a silicon-containing solid solution (Example 11).
[図 42]ケィ素含有固溶体から得られた最終生成物の電子顕微鏡写真である ( 実施例 1 1 ) 。 FIG. 42 is an electron micrograph of the final product obtained from the silicon-containing solid solution (Example 11).
[図 43]実施例 1 1及び実施例 2の最終生成物の粉末 X線回折の結果である。 FIG. 43 shows the results of powder X-ray diffraction of the final products of Example 1 and Example 2.
[図 44]廃アスベストの溶融スラグの電子顕微鏡写真である (参考例 2 ) 。 [Fig.44] An electron micrograph of molten asbestos molten slag (Reference Example 2).
[図 45]参考例 2の溶融スラグから得られた最終生成物の電子顕微鏡写真であ る (実施例 1 2 ) 。 FIG. 45 is an electron micrograph of the final product obtained from the molten slag of Reference Example 2 (Example 12).
[図 46]参考例 2の溶融スラグ、 実施例 1 2の最終生成物及び参考例 1の廃ァ スべス卜の粉末 X線回折の結果である。 FIG. 46 shows the results of powder X-ray diffraction of the molten slag of Reference Example 2, the final product of Example 12 and the waste base of Reference Example 1.
[図 47]廃アスペスト及びアルミン酸ナトリゥ厶からの最終生成物の電子顕微 鏡写真である (比較例 1 ) 。 FIG. 47 is an electron micrograph of the final product from waste asbestos and sodium aluminate (Comparative Example 1).
[図 48]廃アスペストの溶融スラグからの最終生成物の電子顕微鏡写真である (比較例 2 ) 。 FIG. 48 is an electron micrograph of the final product from the molten slag of waste asbestos (Comparative Example 2).
[図 49]廃アスペス卜の溶融スラグ及び廃アルミニウムからの最終生成物の電 子顕微鏡写真である (実施例 1 3 ) 。 FIG. 49 is an electron micrograph of the final product from the molten slag of waste asbestos and waste aluminum (Example 13).
[図 50]無害化した岩石状の廃アスペスト溶融物、 及びこれを粉状に粉砕した ものの外観写真である (実施例 1 4 ) 。 FIG. 50 is a photograph of the appearance of a detoxified rock-like waste aspaste melt and a powder of this as ground (Example 14).
[図 51 ]アルミン酸ナトリゥムと無害化廃アスペスト溶融物粉末とを重量比 1 : 1で混合し、 8 0 0 °Cで加熱処理して得られた生成物の外観写真である ( 実施例 1 4) 。 [FIG. 51] An appearance photograph of a product obtained by mixing sodium aluminate and detoxified waste aspaste melt powder at a weight ratio of 1: 1 and heat-treating at 800 ° C. ( Example 1 4).
[図 52]アルミン酸ナトリゥ厶と無害化廃アスペスト溶融物粉末とを重量比 1 : 1で混合し、 1 200°Cで加熱処理して得られた生成物の外観写真である (実施例 1 4) 。 FIG. 52 is an appearance photograph of a product obtained by mixing sodium aluminate and detoxified waste aspaste melt powder at a weight ratio of 1: 1 and heat-treating at 1 200 ° C. (Example 1) Four) .
[図 53]ケィ酸カルシウムと無害化廃アスベスト溶融物粉末とを重量比 1 : 1 で混合し、 1 200°Cで加熱処理して得られた生成物の外観写真である (実 施例 1 4) 。 [Fig. 53] An appearance photograph of a product obtained by mixing calcium silicate and detoxified waste asbestos melt powder at a weight ratio of 1: 1 and heat-treating at 1 200 ° C (Example 1) Four) .
[図 54]ケィ酸カルシウムに酸化アルミニウムを 1 5%混合したものと、 無害 化廃アスベスト溶融物粉末とを重量比 1 : 1で混合し、 1 200°Cで加熱処 理して得られた生成物の外観写真である (実施例 1 4) 。 [Fig.54] Obtained by mixing 15% of aluminum oxide with calcium silicate and detoxified waste asbestos melt powder at a weight ratio of 1: 1, and heat treatment at 1 200 ° C It is the external appearance photograph of a product (Example 14).
[図 55]無害化廃アスペスト溶融物粉末に酸化アルミニウムを 1 5%混合し、 1 200°Cで加熱処理して得られた生成物の外観写真である (実施例 1 4) FIG. 55 is an external appearance photograph of a product obtained by mixing 15% of aluminum oxide with detoxified waste aspaste melt powder and heat-treating it at 1 200 ° C. (Example 14)
Claims
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2008501637A JP5272156B2 (en) | 2006-02-22 | 2007-02-22 | Method for detoxifying waste asbestos, method for producing zeolite and production intermediate thereof |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2006046048 | 2006-02-22 | ||
| JP2006-046048 | 2006-02-22 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2007097124A1 true WO2007097124A1 (en) | 2007-08-30 |
Family
ID=38437168
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/JP2007/000116 Ceased WO2007097124A1 (en) | 2006-02-22 | 2007-02-22 | Treatment method for converting waste asbestos into harmless products, process for production of zeolite, and intermediates for the production |
Country Status (2)
| Country | Link |
|---|---|
| JP (1) | JP5272156B2 (en) |
| WO (1) | WO2007097124A1 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116060096A (en) * | 2021-10-29 | 2023-05-05 | 中国石油化工股份有限公司 | A kind of catalytic cracking auxiliary agent and its preparation method and application |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH06134438A (en) * | 1992-10-29 | 1994-05-17 | Kanagawa Pref Gov | Method for treating waste asbestos material and manufacture of ceramic product using the same |
| JP2000290011A (en) * | 1999-04-09 | 2000-10-17 | Aisin Takaoka Ltd | Inorganic porous body and its production |
| JP2002173320A (en) * | 2000-12-06 | 2002-06-21 | Ikuhiro Ando | Synthetic method of zeolite by induction and zeolite composition |
| JP2003094006A (en) * | 2001-09-26 | 2003-04-02 | A & A Material Corp | Method for treating asbestos and products thereof |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4189730B2 (en) * | 2002-10-18 | 2008-12-03 | 株式会社エーアンドエーマテリアル | Non-asbestos processing method of asbestos slate |
-
2007
- 2007-02-22 WO PCT/JP2007/000116 patent/WO2007097124A1/en not_active Ceased
- 2007-02-22 JP JP2008501637A patent/JP5272156B2/en not_active Expired - Fee Related
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH06134438A (en) * | 1992-10-29 | 1994-05-17 | Kanagawa Pref Gov | Method for treating waste asbestos material and manufacture of ceramic product using the same |
| JP2000290011A (en) * | 1999-04-09 | 2000-10-17 | Aisin Takaoka Ltd | Inorganic porous body and its production |
| JP2002173320A (en) * | 2000-12-06 | 2002-06-21 | Ikuhiro Ando | Synthetic method of zeolite by induction and zeolite composition |
| JP2003094006A (en) * | 2001-09-26 | 2003-04-02 | A & A Material Corp | Method for treating asbestos and products thereof |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116060096A (en) * | 2021-10-29 | 2023-05-05 | 中国石油化工股份有限公司 | A kind of catalytic cracking auxiliary agent and its preparation method and application |
Also Published As
| Publication number | Publication date |
|---|---|
| JP5272156B2 (en) | 2013-08-28 |
| JPWO2007097124A1 (en) | 2009-07-09 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Paolini et al. | Asbestos treatment technologies | |
| Zhong et al. | The adsorption mechanism of heavy metals from coal combustion by modified kaolin: Experimental and theoretical studies | |
| TW408087B (en) | Process for preparing environmentally stable products by the remediation of contaminated sediments and soils | |
| Zhang et al. | Stabilization/solidification of municipal solid waste incineration fly ash via co-sintering with waste-derived vitrified amorphous slag | |
| CN111732353B (en) | Method for treating sand-based waste incineration fly ash by using cement kiln in cooperation | |
| Erol et al. | The influence of the binder on the properties of sintered glass-ceramics produced from industrial wastes | |
| Gong et al. | Effects of microwave-assisted thermal treatment on the fate of heavy metals in municipal solid waste incineration fly ash | |
| CN105032890B (en) | Barium slag disposal system and processing method | |
| JP7027672B2 (en) | Molten slag treatment method, mesoporous silica production method, and silica production method | |
| Long et al. | Effective disposal of hazardous waste from non-ferrous waste recycling through thermal treatment | |
| CN113913619A (en) | Method for efficiently removing nitrogen from secondary aluminum ash and preparing premelted calcium aluminate refining agent | |
| WO2009147834A1 (en) | Method of detoxifying asbestos-containing solid waste | |
| US8470087B2 (en) | Production method for a lightweight construction material using asbestos waste | |
| JP2002177924A (en) | Detoxification treatment process of incineration ash by diffusing and decomposing incineration ash atoms and equipment for the same process | |
| Guerrero et al. | Hydrothermal treatment of fly ash from municipal solid waste incineration | |
| WO2007097124A1 (en) | Treatment method for converting waste asbestos into harmless products, process for production of zeolite, and intermediates for the production | |
| WO2001012352A1 (en) | Method for treating hazardous material | |
| AU749436B2 (en) | Method of treating spent potliner material from aluminum reduction cells | |
| Lukita et al. | Utilization of hazardous waste of black dross aluminum: processing and application-a review. | |
| CN115611657B (en) | Lightweight aggregate with aluminum ash as raw material and preparation method thereof | |
| JP2001342045A (en) | Method of manufacturing cement clinker | |
| AU4326300A (en) | Method of recovering fumed silica from spent potliner | |
| Gautam et al. | Calcium oxide: Synthesis and applications | |
| WO2006090955A1 (en) | Method for synthesizing zeolite using coal-fired powerplant bottom ash | |
| KR20110091169A (en) | Manufacturing method of cement using fly ash and purified sludge |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| 121 | Ep: the epo has been informed by wipo that ep was designated in this application | ||
| DPE1 | Request for preliminary examination filed after expiration of 19th month from priority date (pct application filed from 20040101) | ||
| ENP | Entry into the national phase |
Ref document number: 2008501637 Country of ref document: JP Kind code of ref document: A |
|
| NENP | Non-entry into the national phase |
Ref country code: DE |
|
| 122 | Ep: pct application non-entry in european phase |
Ref document number: 07713498 Country of ref document: EP Kind code of ref document: A1 |
|
| DPE1 | Request for preliminary examination filed after expiration of 19th month from priority date (pct application filed from 20040101) |