JP2013088102A - Fluorine-containing waste treatment method, and fluorine-containing waste treatment apparatus - Google Patents

Abstract

PROBLEM TO BE SOLVED: To provide a fluorine-containing waste treatment method and fluorine-containing waste treatment apparatus, by and with which fluorine-containing waste can be treated without requiring fuel separately, and fuel gas can be collected from other waste and effectively used.SOLUTION: The fluorine-containing waste treatment apparatus includes: a compression device 20 which compresses waste in batch and molds a compressed block; a gasification melting furnace 50 having a thermal decomposition portion 52, a gas reforming part 53 and a melting part 54; a supply device 40 which supplies the compressed block and fluorine-containing liquid wastes to the thermal decomposition part 52; a gas refining device 80 which refines the reformed gas reformed by the gas reforming part 53 by washing with wash water to recover as fuel gas; and a wash water treating device 90 which removes fluorine from the wash water after the reformed gas is washed by the gas refining device 80. The thermal decomposition part 52 subjects the compressed block P and fluorine-containing liquid wastes to thermal decomposition and gasification, the gas reforming part 53 reforms produced gas, and the melting part 54 melts and discharges non-inflammable substances of the compressed block P and fluorine-containing wastes.

Description

  The present invention relates to a fluorine-containing waste treatment method and a fluorine-containing waste treatment apparatus capable of efficiently and economically treating fluorine-containing waste.

  Fluorine-based organic compounds are chemically very stable, and are therefore widely used in various applications such as surfactants, water repellents, surface treatment agents, and coating agents.

<PFOS>
Among the fluorine-based organic compounds, perfluoroalkylsulfonic acids such as perfluorocarboxylic acids (PFCAs) and perfluorooctane sulfonic acid (PFOS) are used as the surface of semiconductors and metal plating as water and oil repellents and surfactants. It is used in many industries such as treating agents and fire extinguishing agents. However, it is difficult to be decomposed in the natural environment due to its chemical stability, it is widely present in the environment such as the natural world and society, and its accumulation in living organisms has also been clarified, and has come to be noted as a new environmental pollutant .

  Nine substances including PFOS were newly adopted in 2009 as target substances of the Stockholm Convention on Persistent Organic Pollutants (International Convention to Eliminate Hazardous Substances Easily Accumulated in Living Organisms) Recommendations restricting manufacturing, use, import and export were adopted. In response to this recommendation, PFOS has been designated as a Class 1 Specified Chemical Substance in the “Law Concerning the Examination and Regulation of Chemical Substances” (Chemical Substances Control Law) in Japan, and PFOS production and import are prohibited in principle. Production of contained products was also prohibited.

  PFOS-containing products manufactured before such regulations are present as fire extinguishing agents, semiconductor resist solutions, and the like, and the processing when discarding PFOS-containing products is a problem. In order to deal with this problem, the disposal of PFOS-containing materials shall be conducted through a demonstration test using the waste to be treated in accordance with “Technical considerations regarding the treatment of PFOS-containing waste” (March 2011). Therefore, it is supposed to be done at the establishment where it was confirmed that it can be properly disassembled.

In the above-mentioned “Technical considerations regarding treatment of PFOS-containing waste”, the decomposition rate and emission target to be achieved during the decomposition treatment of PFOS-containing waste are defined as follows.
Decomposition rate of PFOS: 99.999% or higher Residual concentration of PFOS or its salt in wastewater generated by decomposition treatment: 2 μg / L or less Residual concentration of PFOS or its salt in residue generated by decomposition treatment: 3 mg / kg or less Decomposition Hydrogen fluoride concentration in exhaust gas generated by treatment: 5 mg / m ³ N or less Hydrogen fluoride concentration in wastewater generated by decomposition treatment: 8 mg / L or less (except for sea areas)
15mg / L or less (sea area)

<Freon Gas>
In addition, other fluorine-based organic compounds such as chlorofluorocarbon (CFC), hydrochlorofluorocarbon (HCFC), and hydrofluorocarbon (HFC) have been used as refrigerants and foaming agents. It has become clear that it is a substance that pollutes the global environment, such as effect gases, and there is a need for the recovery and decomposition of CFCs. A heat insulating material such as a foamed urethane material contains chlorofluorocarbon used as a foaming agent, and it is regulated that chlorofluorocarbon gas is reliably decomposed during the treatment of urethane foam waste.

  Non-Patent Document 1 discloses a decomposition method in which PFOS-containing waste is incinerated in a rotary kiln furnace.

DOWA Ecosystem Co., Ltd., PFOS waste disposal, [online], [October 5, 2011 search], Internet, <http://www.dowa-eco.co.jp/business/ waste / pfos.html>

  In the system according to Non-Patent Document 1, fluorine-containing waste can be incinerated and decomposed. However, there is a problem that fuel is necessary to heat the inside of the rotary kiln furnace, and the processing cost increases. Further, since the rotary kiln furnace is an incinerator, there is a problem that when fluorine-containing waste is incinerated with other waste, fuel gas cannot be recovered from the other waste and effectively used. .

  In view of such circumstances, the present invention can treat fluorine-containing waste efficiently and economically without the need for a separate fuel, and when treating fluorine-containing waste together with other waste, the present invention It is an object of the present invention to provide a fluorine-containing waste processing method and a fluorine-containing waste processing apparatus capable of recovering fuel gas from other waste and effectively using it.

<First invention>
In the method for treating fluorine-containing waste according to the present invention, fluorine-containing liquid waste is rendered harmless by a vertical gasification and melting furnace, and other waste is gasified and recovered as fuel gas.

  In such a method for treating fluorine-containing waste, in the present invention, the above-mentioned other waste is batch-compressed to form a compression block, and the fluorine-containing liquid waste is combined with the compression block in a vertical gasification melting furnace. It is supplied to the pyrolysis section and pyrolyzed and gasified, and the generated gas is gas reformed in the gas reforming section of the vertical gasification melting furnace, and the incombustible material is melted in the melting section of the vertical gasification melting furnace. Fluorine is generated from the gasification and melting process to be discharged, the gas purification process in which the gas-reformed reformed gas is purified by washing with cleaning water and recovered as fuel gas, and the cleaning water in which the reformed gas is washed in the gas purification process. And a cleaning water treatment step to be removed.

<Second invention>
In the method for treating fluorine-containing waste according to the present invention, fluorine-containing solid waste is detoxified by a vertical gasification melting furnace and other waste is gasified and recovered as fuel gas.

  In such a method for treating fluorine-containing waste, in the present invention, the compression step of batch-compressing a mixture of fluorine-containing solid waste and the above-mentioned other waste to form a mixture compression block, and the mixture compression block as a vertical type Pyrolysis and gasification is supplied to the pyrolysis section of the gasification melting furnace, the generated gas is gas reformed in the gas reforming section of the vertical gasification melting furnace, and the incombustible material is converted into the vertical gasification melting furnace. The gasification and melting process that melts and discharges in the melting part of the gas, the gas purification process that purifies the reformed gas that has been gas-reformed with cleaning water and recovers it as fuel gas, and the reformed gas is cleaned in the gas purification process And a cleaning water treatment step for removing fluorine from the cleaning water.

  Further, in the method for treating fluorine-containing waste according to the first and second inventions, the washing water treatment step may add the calcium compound to the washing water and precipitate and separate calcium fluoride to remove fluorine. .

Further, in the method for treating fluorine-containing waste according to the first and second inventions, the cleaning water contains SiO ₂ , and the cleaning water treatment step adds potassium compounds to the cleaning water to precipitate potassium silicofluoride. It is good also as separating and removing a fluorine.

<Third invention>
The treatment apparatus for fluorine-containing waste according to the present invention renders fluorine-containing liquid waste harmless and gasifies other waste and collects it as fuel gas.

  In such a fluorine-containing waste treatment apparatus, in the present invention, a vertical gas having a compression apparatus for batch-compressing the other waste and forming a compression block, and a thermal decomposition section, a gas reforming section, and a melting section. A melting gas furnace, a compression block, a supply device for supplying a fluorine-containing liquid waste to the thermal decomposition section, and a reformed gas that has been gas-reformed in the gas reforming section by washing with cleaning water for purification and fuel gas And a cleaning water treatment device that removes fluorine from the cleaning water that has been cleaned of the reformed gas by the gas purification device, and the thermal decomposition section of the vertical gasification melting furnace includes a compression block and fluorine It is characterized by pyrolyzing and gasifying the contained liquid waste, the gas reforming unit gas reforms the generated gas, and the melting unit melts and discharges the incombustibles of the compression block and fluorine-containing liquid waste It is said.

<Fourth Invention>
The treatment apparatus for fluorine-containing waste according to the present invention renders fluorine-containing solid waste harmless and gasifies other waste and collects it as fuel gas.

  In such a fluorine-containing waste treatment apparatus, in the present invention, a compression apparatus, a thermal decomposition section, a gas reformer, and the like that batch-compress a mixture of fluorine-containing solid waste and the above-mentioned other waste to form a mixture compression block. Vertical gasification and melting furnace having a mass part and a melting part, a supply device for supplying a mixture compression block to the thermal decomposition part of the vertical gasification and melting furnace, and gas reformed by the gas reforming part The above vertical gasification is equipped with a gas purification device that cleans and purifies gas with cleaning water and collects it as fuel gas, and a cleaning water treatment device that removes fluorine from the cleaning water that has been cleaned of the reformed gas by the gas purification device. The pyrolysis section of the melting furnace pyrolyzes and gasifies the mixture compression block, the gas reforming section gas-reforms the generated gas, and the melting section melts and discharges incombustibles in the mixture compression block. It is said.

  In the first to fourth inventions, the gas reforming means that at least hydrogen gas and carbon monoxide that are useful as fuel gas are produced by reacting the hydrocarbon gas contained in the gas generated by pyrolysis and gasification with water vapor. And the thermal decomposition of the tar content contained in the generated gas.

  In the first invention to the fourth invention, since the thermal energy generated by burning combustible materials contained in other waste is used to thermally decompose fluorine-containing waste, in order to thermally decompose fluorine-containing waste There is no need to prepare additional fuel. Further, the gas generated by pyrolyzing and gasifying the other waste is subjected to gas reforming and then refined and recovered as fuel gas.

  In the present invention, fluorine-containing waste can be efficiently and economically processed without requiring a separate fuel, and fuel gas can be recovered from other waste and effectively used.

It is a block diagram which shows the outline of a structure of the processing apparatus of the fluorine-containing liquid waste which concerns on 1st embodiment of this invention. It is a block diagram which shows the process of the gas purification which concerns on 1st embodiment of this invention, and a washing water process. It is a block diagram which shows the process of the gas purification which concerns on 2nd embodiment of this invention, and a washing water process.

<First embodiment>
In the present embodiment, an embodiment in which the fluorine-containing waste to be treated is a fluorine-containing liquid waste will be described. Examples of the fluorine-containing liquid waste include perfluoroalkyl sulfonic acids such as perfluorooctane sulfonic acid (PFOS) and perfluorocarboxylic acids (PFCAs). Before describing the specific configuration of the treatment apparatus according to the present embodiment, first, an outline of the treatment of fluorine-containing liquid waste by the treatment apparatus will be described.

  The treatment apparatus is an apparatus for detoxifying the fluorine-containing liquid waste and gasifying other waste and recovering it as fuel gas. In the processing apparatus, first, the other waste is compressed batchwise in a compression apparatus to form a compression block, and then the fluorine-containing liquid waste is heated together with the compression block to the heat of the vertical gasification melting furnace. Supply to the disassembly unit. As said other waste, the waste containing fixed carbon is preferable. Here, “fixed carbon” refers to carbon that does not volatilize even when heated. In the pyrolysis section, an oxygen-containing gas is introduced, and the compressed block and the fluorine-containing liquid waste are pyrolyzed and gasified into carbon monoxide, hydrogen, and the like.

  In addition, an oxygen-containing gas is introduced in the gas reforming section of the vertical gasification melting furnace, the gas generated in the thermal decomposition section is gas reformed, and the reformed gas is washed and purified by a gas purifier. Recover as fuel gas. Moreover, in a melting part, a compression block and the incombustible material of a fluorine-containing liquid waste are fuse | melted, and it discharges | emits as molten slag and molten metal.

  FIG. 1 is a block diagram showing an outline of the configuration of a fluorine-containing liquid waste treatment apparatus 1 according to this embodiment. Hereinafter, the configuration of the processing apparatus 1 will be described with reference to FIG.

  As shown in FIG. 1, the processing apparatus 1 is provided with a waste input apparatus 10 that inputs the other waste from above into a compression apparatus 20 described later. The waste input device 10 includes a hopper 11 that receives and stores waste from the outside, and a lid 12 that forms the bottom of the hopper 11 and can be freely opened and closed. The waste input device 10 inputs the waste into the compression device 20 when the lid 12 is in the open position.

  Below the waste input device 10, there is provided a compression device 20 for compressing the waste and forming a compression block. The compression device 20 includes a cylindrical portion 21 that extends horizontally at a position below the hopper 11, a piston 22 that reciprocates in the cylindrical portion 21 in the front-rear direction (left-right direction in FIG. 1), and the hopper 11. And a plate-like compression support plate 23 that reciprocates in the vertical direction at the downstream position (right side in FIG. 1) to open and close the downstream opening of the tubular portion 21. The cylindrical portion 21 has an inner wall section having the same shape and the same dimension as an inner wall section of a heating furnace 30 described later.

  In the compression device 20, the piston 22 moves forward (rightward) toward the compression support plate 23 in a state where the compression support plate 23 closes the downstream opening of the cylindrical portion 21 at the lowered position. The waste introduced from the hopper 11 is sandwiched and compressed between the piston 22 and the compression support board 23 in the front-rear direction, and the waste compression block P is formed. The compression block P is formed batchwise.

  A tunnel-type heating furnace 30 (hereinafter referred to as “heating furnace 30”) connected to the cylindrical portion 21 of the compression apparatus 20 extends in the horizontal direction on the downstream side of the compression apparatus 20. The heating furnace 30 is heated from the outside, and the compression block P supplied from the compression device 20 is dried in the heating furnace 30. The downstream end of the heating furnace 30 is connected to an inlet 51 of a vertical gasification and melting furnace 50 (hereinafter referred to as “gasification and melting furnace 50”). It can be supplied into the chemical melting furnace 50. Further, the upper wall of the heating furnace 30 is inclined upward toward the downstream side (right side in FIG. 1), and the passage is widened. As a result, a space is formed above the compression block P, and the water evaporated from the compression block P can be released.

  The processing apparatus 1 is provided with a supply device 40 for supplying fluorine-containing liquid waste into the gasification melting furnace 50. The supply device 40 includes a tank 41 for storing fluorine-containing liquid waste, and a pump 42 for feeding the fluorine-containing liquid waste from the tank 41. In the present embodiment, the fluorine-containing liquid waste is fed by the pump 42 to a position in front of the inlet 51 of the gasification melting furnace 50. As will be described later, the fed fluorine-containing liquid waste is supplied into the gasification melting furnace 50 together with the compression block P.

  The gasification melting furnace 50 has a vertical portion extending in the vertical direction and a horizontal portion extending in the horizontal direction from the lower portion of the vertical portion. The portion extending in the vertical direction has a substantially lower half portion formed as a thermal decomposition portion 52 and a substantially upper half portion formed as a gas reforming portion 53. Further, the horizontal portion is formed as a melting portion 54.

  In the thermal decomposition section 52, the compressed block P and fluorine-containing liquid waste are deposited to form a waste deposit layer Q, and the waste of the compressed block P and the fluorine-containing liquid waste forming the waste deposit layer Q are formed. The material is gasified by thermal decomposition and the incombustible component is melted. A first oxygen-containing gas supply port 55 for supplying an oxygen-containing gas into the waste accumulation layer Q is provided at the lower part of the side wall of the gasification melting furnace 50. When the fluorine-containing liquid waste is thermally decomposed in the thermal decomposition unit 52, hydrogen and CO are generated and hydrogen fluoride is generated.

  In the gas reforming unit 53, as will be described later, the gas generated from the waste accumulation layer Q in the thermal decomposition unit 52 is reformed to generate a reformed gas. A plurality of second oxygen-containing gas supply ports 56 for supplying an oxygen-containing gas into the gas reforming unit 53 are provided on the upper side of the side wall of the gasification melting furnace 50.

  In the melting part 54, the melt generated in the thermal decomposition part 52 is heated, and carbon and the like contained in the melt are gasified and removed. A fuel gas supply port 57 for supplying fuel gas to the melting portion 54 is provided on the upper wall of the horizontal portion of the gasification melting furnace 50. Further, a melt discharge port 58 for discharging the melt to the outside is provided in the melt section 54 so as to extend downward.

  A gas duct 60 is provided at the top of the gasification melting furnace 50 and extends from a reformed gas discharge port 59 formed at the top to discharge the reformed gas generated in the gas reforming unit 53 to the outside of the furnace. Yes. On the downstream side of the gas duct 60, a cooling and washing water circulation device 70 for cooling and washing the reformed gas is provided. The cooling and washing water circulation device 70 is connected to the gas duct 60 and cools the reformed gas with the cooling washing water and removes water-soluble components, dust, carbon fine particles and the like from the reformed gas, Cooling and washing water used for cooling and washing the reformed gas in the cooling and washing apparatus 71 is stored, and a precipitation tank 72 for precipitating and separating solids contained in the cooling and washing water, and cooling from which the solids are separated. And a heat exchanger 73 for cooling the washing water. The cooled cooling cleaning water is returned to the cooling cleaning device 71 again.

  Further, on the downstream side of the cooling and cleaning device 71, a gas purification device 80 for purifying the reformed gas cooled and cleaned by the cooling and cleaning device 71 to generate a purified gas that can be used as fuel gas is provided. Yes. The gas purification device 80 includes an acid cleaning device 81 that dissolves and removes heavy metals from the reformed gas cooled and cleaned by the cooling and cleaning device 71 with acid cleaning water, and a chloride from the reformed gas with alkaline cleaning water. An alkali cleaning device 82 that removes hydrogen and hydrogen fluoride, a desulfurization device 83 that removes hydrogen sulfide from the reformed gas, and a dehumidifier 84 that removes moisture from the reformed gas are provided.

  The acid cleaning device 81 and the alkali cleaning device 82 of the gas purification device 80 are connected to the cleaning water treatment device 90. As will be described later with reference to FIG. 2, the cleaning water treatment device 90 is configured to remove a part of the acid cleaning water and a part of the alkaline cleaning water used for cleaning the reformed gas, respectively. The components received from the apparatus 82 and dissolved and captured by the acid cleaning apparatus 81 and the alkali cleaning apparatus 82 are removed from the acid cleaning water and the alkali cleaning water.

  Hereinafter, the processing of the fluorine-containing liquid waste by the processing apparatus 1 will be described.

  First, other waste is stored in the hopper 11 of the waste input device 10. The lid 12 provided on the hopper 11 is opened, and a predetermined amount of the waste is put into the compression device 20. The compression device 20 moves the piston 22 forward with the compression support plate 23 brought to the lowered position, whereby the waste is compressed to form a dense compression block P. The compression block P is formed batchwise. The compression block P is sequentially formed, and the compression block P is pushed forward and supplied to the heating furnace 30.

  The cross-sectional shape of the compression block P is the same shape and the same size as the cross section of the inner wall of the inlet of the heating furnace 30, and the compression block P is pushed into contact with the inner wall of the heating furnace 30. Can seal the atmosphere in the furnace. Each time a new compression block is sequentially pushed, the compression block P moves toward the charging port 51 of the gasification melting furnace 50 while sliding in the heating furnace 30.

  As described above, the heating furnace 30 is heated from the outside, the inside is heated, and the moisture in the compression block P is evaporated and dried in the process of moving and raising the temperature of the compression block P. Also, the fluorine-containing liquid waste is sent from the tank 41 to a position before the charging port 51 of the gasification melting furnace 50 by the pump 42. The dried compressed block P and the fluorine-containing liquid waste are charged and supplied from the charging port 51 of the gasification melting furnace 50 into the thermal decomposition section 52 of the gasification melting furnace 50.

  A preferable range of a ratio of the supply amount of the fluorine-containing liquid waste to the compressed block supply amount is obtained in advance, and the fluorine-containing liquid waste is supplied to the thermal decomposition unit 52 at the supply amount. preferable. As a result, the amount of heat energy generated by burning fixed carbon contained in the waste molded as the compressed block P with the oxygen-containing gas can be set to an amount sufficient to thermally decompose the fluorine-containing liquid waste. Because. Further, if the above ratio becomes larger than the preferred range and the supply amount of the fluorine-containing liquid waste increases, it is not preferable because it becomes difficult to obtain the amount of heat energy necessary for pyrolyzing the fluorine-containing liquid waste. .

  The compressed block P and the fluorine-containing liquid waste supplied into the thermal decomposition unit 52 form a waste accumulation layer Q. In the waste accumulation layer Q, an oxygen-containing gas is supplied into the waste accumulation layer Q from a first oxygen-containing gas supply port 55 provided in the lower part of the thermal decomposition unit 52. As a result, combustibles such as fixed carbon in the waste burn, and the waste of the compressed block P and the fluorine-containing liquid waste are thermally decomposed by the thermal energy. By this thermal decomposition, gasification into carbon monoxide, hydrogen, hydrocarbons, carbon dioxide and the like is performed. Further, thermal decomposition of waste and fluorine-containing liquid waste generates hydrogen chloride from the contained chlorine, hydrogen sulfide from the sulfur, and hydrogen fluoride from the fluorine. It has been confirmed that a hardly decomposable fluorine organic material such as PFOS is decomposed by heating at 1100 ° C. or more for 2 seconds or more.

  In the present embodiment, as described above, the heat energy generated by burning combustible materials such as fixed carbon contained in the waste forming the compressed block P is used to thermally decompose the fluorine-containing liquid waste. In addition, it is not necessary to separately prepare a fuel for thermally decomposing fluorine-containing liquid waste, and it can be efficiently and economically processed.

  In addition, the incombustible components (metal, ash, etc.) of the waste and the fluorine-containing liquid waste are melted to generate a melt. In the melting part 54 connected to the lower part of the thermal decomposition part 52, the melt is heated by the high-temperature combustion gas generated by combustion of the fuel gas supplied from the fuel gas supply port 57, and a trace amount contained in the melt. The carbon and the like are gasified and removed, and the melt is discharged from the melt outlet 58 as molten slag and molten metal.

  In the gas reforming section 53 of the gasification melting furnace 50, an oxygen-containing gas is supplied from the second oxygen-containing gas supply port 56, and a part of the generated gas from the waste accumulation layer Q is burned to change the temperature atmosphere. The generated gas is retained in the region set to 1000 ° C. or higher, and the following gas reforming is performed.

In the waste accumulation layer Q of the pyrolysis section 52, hydrocarbons (such as methane) and carbon monoxide contained in the generated gas generated by thermal decomposition of the compressed block P and the fluorine-containing liquid waste are gas modified. The mass part 53 reacts with water vapor contained in the generated gas as shown in (1) and (2) below, and is reformed to contain a large amount of carbon monoxide and hydrogen useful as fuel gas.
CH ₄ + H ₂ O → CO + 3H ₂ (1)
CO + H ₂ O → H ₂ + CO ₂ (2)

  When the weight ratio of the water in the waste of the compressed block P supplied to the thermal decomposition unit 52 is 20% by weight or more, the generated gas contains sufficient water vapor, so the reactions (1) and (2) above Is preferable, and a reformed gas having a preferable composition as a fuel gas can be obtained.

In addition, when the weight ratio of water in the waste is less than 20% by weight, the amount of water vapor is small, so that the reactions (1) and (2) are difficult to be performed. A large amount of fine particles are generated, and scum is generated in the cooling and cleaning device 71. In the gas purification device 80, the scum adheres to the piping of the device and closes the piping to make continuous operation difficult. Since problems such as adverse effects on properties occur, it is not preferable.
2CO → C + CO ₂ (3)

  Therefore, when the weight ratio of the water in the waste is less than 20% by weight, in order to avoid the above-described problem, a supply device (not shown) for supplying water vapor or water is provided, and the gas reforming is performed. It is preferable to supply water vapor or water to the mass part 53.

  Further, the generated gas from the waste accumulation layer Q is retained in the gas reforming unit 53 in a region where the gas temperature is set to 1100 ° C. or higher, and cracking of the tar contained in the generated gas is performed. Tar cracking means that the high molecular weight component of the tar is thermally decomposed into low molecular weight hydrocarbons or carbon monoxide, and when the reformed gas is used as fuel gas by removing the tar content. Troubles caused by tar can be avoided. Further, the hydrocarbon generated by cracking further reacts with steam to be reformed into carbon monoxide and hydrogen useful as fuel gas.

  Further, in the gas reforming unit 53, the gas generated from the waste accumulation layer Q is retained in a region where the gas temperature is set to 1100 ° C. or higher, and the generated gas contains fluorine-containing liquid waste. The fluorine-containing liquid waste is decomposed to produce hydrogen fluoride. The hydrogen fluoride is removed from the reformed gas by a gas purifier 80 described later.

  The reformed gas generated in the gas reforming unit 53 is discharged from the reformed gas discharge port 59 at the top of the gasification melting furnace 50 to the gas duct 60 and is cooled by the cooling cleaning device 71 with the cooling cleaning water, Solids such as sexual components, dust, and carbon fine particles are washed away by the cooling washing water. The cooling / washing water used for the cooling and cooling of the reformed gas is guided to the settling tank 72 to precipitate and separate the solid matter. The cooling and washing water from which the solid matter has been separated is cooled by the heat exchanger 73 and introduced into the cooling and washing apparatus 71 again.

  The reformed gas cooled and washed by the cooling and cleaning device 71 is guided to the gas purification device 80, and the acid cleaning device 81 dissolves and removes heavy metals from the reformed gas by the acid cleaning water. The reformed gas contains hydrogen fluoride produced by decomposition of fluorine contained in the fluorine-containing waste, and the hydrogen fluoride is absorbed and removed by the alkali cleaning water in the alkali cleaning device 82. Is done. Further, the reformed gas contains hydrogen chloride generated in the gasification of the waste from the chlorine contained in the waste, and this hydrogen chloride is also contained in the alkaline cleaning device 82. And removed with alkaline washing water. Further, hydrogen sulfide in the reformed gas is removed by the desulfurization device 83. Then, the moisture in the reformed gas is removed by the dehumidifier 84. As a result, purified gas that can be used as fuel gas is recovered.

  The acid cleaning water and the alkali cleaning water used for cleaning the reformed gas in the acid cleaning device 81 and the alkali cleaning device 82 are respectively guided to the cleaning water treatment device 90, and the cleaning water treatment device 90 uses the acid cleaning water. The components dissolved and captured by the cleaning device 81 and the alkaline cleaning device 82 are removed from the acid cleaning water and the alkaline cleaning water. Details of the gas purification step in the gas purification device 80 and the cleaning water treatment step in the cleaning water treatment device 90 will be described later with reference to FIG.

  As other waste to be supplied to the gasification melting furnace 50 together with the fluorine-containing liquid waste, it is preferable to use one having a weight ratio of fixed carbon in the waste of 3% by weight or more. This is because the amount of thermal energy generated by burning the fixed carbon in the waste with the oxygen-containing gas in the thermal decomposition unit 52 can be sufficient to thermally decompose the fluorine-containing liquid waste. In addition, by using a fixed carbon having a weight ratio of 5% by weight or more in the waste, the fluorine-containing liquid waste is thermally decomposed and a sufficient amount of thermal energy is obtained to thermally decompose the waste. Is more preferable.

  If the oxygen-containing gas supplied to the pyrolysis section 52 and the gas reforming section 53 has a large amount of components such as nitrogen other than oxygen, the amount of nitrogen is included in the fuel gas as it is, and the properties as the fuel gas are lowered. Therefore, it is preferable that the oxygen-containing gas to be supplied has a high concentration with an oxygen concentration of 80% by volume or more.

  Next, the reforming of the reformed gas in the gas purification device 80 and the treatment in the washing water treatment device 90 for the washing water used for the gas purification will be described.

  FIG. 2 is a block diagram showing purification gas reforming and treatment of cleaning water used for gas purification in the present embodiment. FIG. 2 shows a gas purification process for generating a purified gas by cleaning the reformed gas with acid cleaning water and alkali cleaning water, and cleaning water for treating the acid cleaning water and the alkali cleaning water used in the gas purification process. Processing steps are shown.

[Reformed gas]
The reformed gas generated in the gas reforming section 53 of the gasification melting furnace 50 includes hydrogen, carbon monoxide, hydrocarbon combustible gas, hydrogen sulfide (H ₂ S), hydrogen chloride (HCl), and hydrogen fluoride. (HF), iron (Fe), zinc (Zn), lead (Pb) heavy metals, calcium (Ca), magnesium (Mg), etc. derived from the ash component of waste are included.

[Gas purification process]
The gas purification step includes an acid cleaning step for cleaning the reformed gas with acid cleaning water, an alkali cleaning step for cleaning the reformed gas from the acid cleaning step with alkaline cleaning water, and a reforming from the alkali cleaning step. It has a desulfurization process in which a gas is subjected to a desulfurization treatment with a desulfurization liquid, and a dehumidification process in which moisture is removed.

<Acid cleaning process>
In the acid cleaning step, the reformed gas is contacted by spraying acid cleaning water or the like, acid cleaning is performed to clean the reformed gas, heavy metals such as iron, zinc, and lead in the reformed gas, and Calcium and magnesium are dissolved or trapped in the acid cleaning water and removed from the reformed gas, and the removed components are dissolved and contained in the acid cleaning water after cleaning. Prior to the cleaning of the reformed gas, the acid cleaning water is added with hydrochloric acid, so that its pH is less than 7, more preferably less than 5. Thus, by setting the pH of the acid wash water to less than 7 and more preferably less than 5, it becomes possible to effectively dissolve heavy metals such as zinc in the reformed gas in the acid wash water. The lower limit of the pH of the acid cleaning water is not particularly limited, but it is preferable to set the pH to 2 or more from the viewpoint of inhibiting corrosion of an acid cleaning apparatus (not shown) for the acid cleaning process.

  The acid cleaning water used for the gas cleaning in the acid cleaning step is collected and supplied to the acid cleaning step again, whereby the acid cleaning water is circulated and used. In the acid cleaning water used for the gas cleaning, the removed components removed from the reformed gas are accumulated. A part of the acid wash water is extracted and sent to a wash water treatment step, and a removal treatment is performed as described later.

<Alkali cleaning process>
In the alkali cleaning step, the reformed gas cleaned in the acid cleaning step is brought into contact with, for example, sprayed alkali cleaning water to perform alkali cleaning for cleaning the reformed gas, and hydrogen chloride ( HCl) and hydrogen fluoride (HF) are dissolved in alkaline washing water and removed from the reformed gas, and the removed components are dissolved and contained in the alkaline washing water after washing in the form of chlorine ions and fluorine ions.

The alkali cleaning water used for the gas cleaning in the alkali cleaning step is recovered and supplied to the alkali cleaning step again, whereby the alkali cleaning water is circulated and used. The pH of the alkali cleaning water supplied to the alkali cleaning step is adjusted by adding sodium hydroxide (NaOH) prior to the reformed gas cleaning. In addition, the alkaline washing water used for the gas washing in the alkali washing step includes sodium chloride (Na ⁺ , Cl ⁻ ) generated by reacting hydrogen chloride removed from the reformed gas with sodium hydroxide, Sodium fluoride (Na ⁺ , F ⁻ ) produced by the reaction of hydrogen fluoride with sodium hydroxide is accumulated. A part of the alkaline washing water is extracted and sent to the washing water treatment step, and the removal treatment is performed as described later.

<Desulfurization process>
In the desulfurization step, a desulfurization solution containing an iron chelating agent (iron chelate complex) is brought into contact with the reformed gas cleaned in the alkali cleaning step, and hydrogen sulfide (H ₂ S) is removed from the reformed gas. Since a desulfurization method using an iron chelating agent as a desulfurization liquid is known, a description thereof is omitted here. In this embodiment, desulfurization is performed using an iron chelating agent. However, the desulfurization method is not limited to this, and for example, a desulfurization method using sodium naphthoquinonesulfonate, a desulfurization method using picric acid, or the like can be applied. .

<Dehumidification process>
Then, the reformed gas from which hydrogen sulfide has been removed in the desulfurization step has its moisture removed in the dehumidification step and is sent out as a purified gas.

  Thus, the reformed gas is purified through the acid cleaning step, the alkali cleaning step, the desulfurization step, and the dehumidification step. The refined refined gas is used as a fuel gas.

[Washing water treatment process]
Next, a cleaning water treatment process for removing dissolved and trapped components from the acid cleaning water and alkaline cleaning water used in the gas purification process will be described. Components removed from the reformed gas are accumulated in the acid cleaning water and alkaline cleaning water used for cleaning the reformed gas in the gas purification process. In the cleaning water treatment process, the acid cleaning water and alkali cleaning water are used. The components removed from the reformed gas are removed from the water.

  The washing water treatment process includes an acid washing water solid-liquid separation process, a mixing process, a fluorine removal process, an iron removal process, a zinc / lead removal process, a calcium / magnesium removal process, a concentration process, and a crystallization process. Hereinafter, each step will be described.

<Solid-liquid separation process of acid wash water>
In the solid-liquid separation process of the acid cleaning water, the acid cleaning water extracted from the acid cleaning process is separated into solid and liquid, and the supernatant water is recycled and used as the acid cleaning water for the acid cleaning process, and the remaining acid cleaning water is supplied to the mixing process. To do. The form of the solid-liquid separator is not particularly limited, and a membrane separator using a specific gravity sedimentation separator, a centrifugal separator, a filtration device, a microfiltration membrane device, an ultrafiltration membrane device, or the like can be used. . The same applies to the solid-liquid separator used in the steps described later. In addition, as shown in FIG. 1, the acid cleaning water extracted from the acid cleaning device 81 may be supplied to a precipitation tank 72 that separates solids from the cooling cleaning water extracted from the cooling cleaning device 71, and solid-liquid separation may be performed.

<Mixing process>
In the mixing step, the acid wash water that has been subjected to the solid-liquid separation process in the solid-liquid separation step and the alkali wash water partially extracted from the alkali wash step are mixed to obtain mixed wash water. As described above, sodium chloride and fluorine ions are accumulated in the alkaline washing water. The mixed washing water contains sodium chloride as a by-product salt as a main component, and includes heavy metals such as iron, zinc, and lead, calcium, magnesium, and fluorine ions.

<Fluorine removal process>
In the fluorine removal step, calcium chloride is added to the mixed washing water in a reaction tank (not shown) for the fluorine removal step, and calcium fluoride is generated and precipitated by reaction with fluorine ions. And the said calcium fluoride is separated and removed as solid content with the solid-liquid separation apparatus (not shown) for a fluorine removal process. The mixed washing water from which the solid content has been separated is supplied to the iron removal step.

  In the mixing process described above, calcium ions contained in the acid wash water react with fluorine ions in the alkaline wash water to produce calcium fluoride. The amount of calcium ions contained in the acid wash water Since the amount is not sufficient with respect to the amount of fluorine ions, calcium chloride is added in the fluorine removing step. Here, it is preferable to add calcium chloride so that the amount of calcium is 1 to 3 times the stoichiometric amount with respect to the amount of fluorine ions in the mixed washing water. At that time, the calcium amount including the calcium amount contained in the acid wash water is used. When it is less than 1 time, fluorine ions remain unreacted, and when it is more than 3 times, unnecessary calcium ions increase, which is not suitable.

  As calcium supplied in the fluorine removing step, calcium chloride is preferable to slaked lime. Addition of slaked lime is not suitable because not only the pH of the mixed washing water becomes too high, but also a large amount of solid matter is generated.

  Since calcium fluoride generated by the reaction with calcium is a fine particle, it takes time to remove the precipitate. In order to accelerate the precipitation removal of calcium fluoride, an excessive amount of calcium is added in the fluorine removal step, and in the calcium / magnesium removal step described later, the excess calcium is precipitated as calcium carbonate, so that the calcium fluoride fine particles are shared. By subsiding, removal is facilitated. In order to perform coprecipitation removal in this way, the stoichiometric ratio of calcium and fluorine is preferably 1.5 or more.

<Iron removal process>
The reformed gas before cleaning contains iron, and the gasification in the gasification and melting furnace is performed in a reducing atmosphere. In other words, iron that is dissolved in the acid cleaning water in the acid cleaning step, in other words, For example, iron contained in the mixed washing water supplied to the iron removal step is mainly divalent ferrous ions (Fe ²⁺ ).

In a reaction tank (not shown) for the iron removal step, an oxidizing agent such as hydrogen peroxide (H ₂ O ₂ ) is added to the raw salt water containing ferrous ions. Divalent ferrous ions (Fe ²⁺ ) contained in the mixed washing water are oxidized by this oxidizing agent to generate trivalent ferric ions (Fe ³⁺ ). As the oxidizing agent, not only hydrogen peroxide but also hypochlorous acid, ozone, and the like can be used.

Next, sodium hydroxide (NaOH) is added to react ferric ions (Fe ³⁺ ) with the sodium hydroxide to precipitate iron hydroxide (Fe (OH) ₃ ). The mixed washing water on which the iron hydroxide is deposited is supplied to a solid-liquid separation device (not shown) for the iron removal step, and the iron hydroxide is separated and removed as a solid content. The mixed washing water from which the solid content has been separated is supplied to the zinc / lead removal step.

<Zinc and lead removal process>
In the zinc / lead removal step, sodium hydroxide is added to the mixed washing water in a reaction tank (not shown) for the zinc / lead removal step so that the pH of the mixed washing water becomes 7.5-10. The zinc ions and lead ions in the mixed washing water are precipitated as hydroxides, that is, zinc hydroxide (Zn (OH) ₂ ) and lead hydroxide (Pb (OH) ₂ ). Then, these hydroxides are separated and removed as a solid content by a solid-liquid separation device (not shown) for the zinc / lead removal step. The mixed washing water from which the solid content has been separated is supplied to the calcium / magnesium removal step.

<Calcium / magnesium removal process>
In the calcium / magnesium removal step, a carbon dioxide source such as carbon dioxide, sodium hydrogen carbonate, sodium carbonate and carbonate ions is added to the mixed washing water in a reaction tank (not shown) for the calcium / magnesium removal step. Then, by further adding sodium hydroxide to further increase the pH of the mixed washing water, calcium contained in the mixed washing water is calcium carbonate (CaCO ₃ ), and magnesium is magnesium carbonate (MgCO ₃ ). As deposited. Then, calcium carbonate and magnesium carbonate are separated and removed as solids by a solid-liquid separation device (not shown) for the calcium / magnesium removal step. The mixed washing water from which the solid content has been removed is supplied to the concentration step. Further, as described above, in the calcium / magnesium removal step, the calcium fluoride that has not been sufficiently removed by precipitation in the fluorine removal step can be removed by coprecipitation with calcium carbonate.

  Since the reformed gas generated in the gasification melting furnace contains carbon dioxide gas, when carbon dioxide is added to the mixed washing water in the calcium / magnesium removal step, the above-mentioned modification is made as a carbon dioxide source. Carbon dioxide gas may be supplied by blowing quality gas into the mixed cleaning water. When recovering the by-product salt as an industrial salt, the carbonate used as the carbonate source is preferably a sodium salt such as sodium bicarbonate or sodium carbonate in order not to lower the purity of the industrial salt.

<Concentration process>
In the concentration step, concentrated water is generated by concentrating the mixed washing water by reducing the water content. The concentrated water is supplied to the crystallization process. As a concentration method, a method of heating mixed washing water by a multi-effect can and evaporating water, a reverse osmosis membrane, electrodialysis, or the like can be used.

<Crystal crystallization process>
In the crystallization step, the concentrated water is evaporated and concentrated with an evaporator or cooled, so that the concentration of the salt dissolved in the concentrated water is made higher than the saturation solubility to precipitate salt crystals, and sodium chloride is crystallized. It is deposited and taken out as a salt slurry. The salt slurry is dehydrated. Most of the impurity components have been removed by the removal process of iron, zinc, lead, calcium, and magnesium described above. However, by performing the crystallization process, the remaining impurities are separated and high purity sodium chloride is removed. It can be obtained as a by-product salt and can be effectively used as an industrial salt. It is preferable to re-apply the calcium removal step of adding and precipitating calcium as calcium carbonate by adding a carbonate source before the crystallization step and further increasing the pH of the mixed washing water by adding sodium hydroxide. . If calcium remains in the concentrated water, calcium fluoride tends to precipitate in the salt crystals obtained by crystallization, and the purity of the by-product salt is lowered, which is not preferable. Moreover, it is preferable to reduce the calcium concentration in the concentrated water before crystallization to 10 mg / L or less.

  In this embodiment, the fluorine-containing liquid waste is supplied to the gasification melting furnace together with the compression block of the other waste. Instead, the fluorine-containing waste as a treatment target is fluorine-containing solid waste. The mixture of the fluorine-containing solid waste and other waste is compressed to form a mixture compression block, and fuel gas is generated from the mixture compression block as in the present embodiment. be able to. In this case, in the processing apparatus shown in FIG. 1, a supply apparatus for supplying the fluorine-containing liquid waste is not essential. Examples of the fluorine-containing solid waste include urethane foam waste containing chlorofluorocarbon gas.

<Second embodiment>
In the first embodiment, the washing water treatment process has one fluorine removal process. However, in this embodiment, the washing water treatment process has another fluorine removal process in addition to the fluorine removal process. This is different from the first embodiment. Since this embodiment is the same as the first embodiment except that there are two fluorine removal steps, the following description will focus on the fluorine removal step with reference to FIG.

FIG. 3 is a block diagram showing purification gas reforming and processing steps for cleaning water used for gas purification in the present embodiment. As seen in FIG. 3, the washing water treatment process has two fluorine removal processes, a first fluorine removal process and a second fluorine removal process, after the mixing process. According to this embodiment, as will be described later, when the acid cleaning water used for cleaning the reformed gas in the acid cleaning step of the gas purification step contains silica (SiO ₂ ) derived from waste In addition, fluorine in the washing water can be effectively removed.

In this embodiment, the acid cleaning water used for cleaning the reformed gas in the acid cleaning step includes iron (Fe), zinc (Zn), lead (Pb), calcium (Ca), and magnesium (Mg). In addition, silica (SiO ₂ ) and potassium (K) derived from waste ash components are contained. In addition, as in the first embodiment, sodium chloride (Na ⁺ , Cl ⁻ ) and sodium fluoride (Na ⁺ , F ⁻ ) are included in the alkaline cleaning water used for cleaning the reformed gas in the alkali cleaning step. include.

<Mixing process>
In the mixing step, silica (SiO ₂ ) contained in the acid wash water and fluorine contained in the alkali wash water are mixed to produce fluoric acid (SiF ₆ ²⁻ ).

<First fluorine removal process>
In the first fluorine removal step, a potassium compound (for example, potassium hydroxide (KOH)) is added to the mixed washing water in a reaction tank (not shown) for the first fluorine removal step, and fluoric acid ions and By this reaction, potassium silicofluoride (K ₂ (SiF ₆ )) is generated and deposited. And the said potassium silicofluoride is separated and removed as solid content with the solid-liquid separator (not shown) for a 1st fluorine removal process.

It is preferable to use a potassium compound as the compound that is reacted with fluoric acid (SiF ₆ ²⁻ ) in the first fluorine removal step to precipitate and precipitate a solid. This is because the sodium compound (such as sodium hydroxide (NaOH)) than to precipitate a) adding sodium silicofluoride the _(Na 2 _(SiF 6)) _also, the solubility of K 2 (SiF ₆₎ is _Na 2 (SiF ₆ This is because the effect of removing fluorine is higher when a potassium compound is used as much.

  When adding the potassium compound in the first fluorine removal step, it is preferable to add the potassium compound so that the amount of potassium is 1 to 3 times the stoichiometric amount with respect to the amount of fluoric acid ions in the mixed washing water. . At this time, since the acid-washed water contains potassium derived from waste, the amount of potassium including the amount of potassium contained in the acid-washed water is set to 1 to 3 times the stoichiometric amount. If it is less than 1 time, fluorine remains unreacted, and if it is more than 3 times, unnecessary potassium ions increase, which is not suitable.

<Second fluorine removal process>
The second fluorine removal step provided after the first fluorine removal step is the same as the fluorine removal step of the first embodiment, and in the reaction tank (not shown) for the second fluorine removal step, Calcium chloride is added to the mixed washing water from which most of the fluorine has been removed by precipitation of potassium silicofluoride in the monofluorine removal step, and calcium fluoride is generated and precipitated by reaction with the remaining fluorine ions. And the said calcium fluoride is separated and removed as solid content with the solid-liquid separator (not shown) for a 2nd fluorine removal process. The mixed washing water from which the solid content has been separated is supplied to the iron removal step. The steps after the iron removal step are the same as the washing water treatment step of the first embodiment shown in FIG.

  In this embodiment, in order to remove most of the fluorine in the first fluorine removal step and to remove the remaining fluorine in the second fluorine removal step, it is possible to more reliably remove the fluorine in the cleaning water. In addition, since the amount of calcium chloride added in the second fluorine removal step can be greatly reduced, the amount of calcium fluoride discharged as a solid content can be reduced, and the processing cost can be reduced.

<Example 1>
In this example, after the fluorine-containing liquid waste (PFOS-containing liquid waste) is treated in the gasification melting furnace shown in FIG. 1 at a gas reforming section temperature of about 1200 ° C., gas generated by gasification is used. The product was rapidly cooled and subjected to acid cleaning and alkali cleaning. As a result, the decomposition rate of PFOS was 99.999% or more, and it was confirmed that the decomposition rate was higher than the decomposition rate to be achieved. In addition, the hydrogen fluoride concentration in the gas after alkali cleaning is 0.05 mg / m ³ N (O ₂ : 12% conversion value), which is the emission target for technical considerations related to the disposal of PFOS-containing waste by the Ministry of the Environment. It was confirmed that it was below 5 mg / m ³ N.

In this example, acid cleaning water and alkaline cleaning water were mixed in the mixing step in the cleaning water treatment step. The calcium concentration in the mixed washing water was about 120 mg / L (about 3 mol-Ca / L), and the fluorine concentration was about 230 mg / L (about 12 mol-F / L). The stoichiometric ratio of calcium fluoride (CaF ₂ ) produced by fluorine and calcium was about 0.5 (Ca / F ₂ ≈0.5). In the fluorine removal step, the fluorine concentration of salt water obtained by precipitating calcium fluoride and solid-liquid separation was 140 mg / L.

<Example 2>
The processing up to the washing water treatment is the same as in the first embodiment. Also in the present example, acid cleaning water and alkaline cleaning water were mixed in the mixing step in the cleaning water treatment step. The calcium concentration in the mixed washing water was about 120 mg / L (about 3 mol-Ca / L), and the fluorine concentration was about 230 mg / L (about 12 mol-F / L). The stoichiometric ratio of calcium fluoride (CaF ₂ ) produced by fluorine and calcium was about 0.5 (Ca / F ₂ ≈0.5).

In the fluorine removal step, a calcium chloride aqueous solution was added to the mixed washing water, and the stoichiometric ratio as CaF ₂ was set to about 1 (Ca / F ₂ ≈1). The fluorine concentration of salt water obtained by precipitating calcium fluoride and solid-liquid separation was about 20 mg / L. Then, in the concentration step, this salt water was concentrated with a multi-effect can and further crystallized in the crystallization step, thereby obtaining a by-product salt. The fluorine concentration of the 10 mass% aqueous solution of by-product salt was about 50 mg / L.

<Example 3>
The processing up to the washing water treatment is the same as in the first embodiment. Also in the present example, acid cleaning water and alkaline cleaning water were mixed in the mixing step in the cleaning water treatment step. The calcium concentration in the mixed washing water was about 120 mg / L (about 3 mol-Ca / L), and the fluorine concentration was about 230 mg / L (about 12 mol-F / L). The stoichiometric ratio of calcium fluoride (CaF ₂ ) produced by fluorine and calcium was about 0.5 (Ca / F ₂ ≈0.5).

In the fluorine removal step, an aqueous calcium chloride solution was added to the mixed washing water, so that the stoichiometric ratio as CaF ₂ was about 1.6 (Ca / F ₂ ≈1.6). In the calcium / magnesium removal process, exhaust gas is diffused into salt water obtained by precipitating calcium fluoride and solid-liquid separation, and by absorbing carbon dioxide in the salt water, calcium carbonate is precipitated, It was further removed by coprecipitation. Then, in the concentration step, this salt water was concentrated with a multi-effect can and further crystallized in the crystallization step, thereby obtaining a by-product salt. The fluorine concentration of the 10 mass% aqueous solution of by-product salt was about 5 mg / L. It was confirmed that the concentration of fluorine contained in the by-product salt can be reduced, impurities can be reduced, and it can be effectively used as industrial salt.

<Example 4>
The processing up to the washing water treatment is the same as in the first embodiment. Also in the present example, acid cleaning water and alkaline cleaning water were mixed in the mixing step in the cleaning water treatment step. The calcium concentration in the mixed washing water was about 120 mg / L (about 3 mol-Ca / L), and the fluorine concentration was about 230 mg / L (about 12 mol-F / L). The stoichiometric ratio of calcium fluoride (CaF ₂ ) produced by fluorine and calcium was about 0.5 (Ca / F ₂ ≈0.5).

In the fluorine removal step, an aqueous calcium chloride solution was added to the mixed washing water, so that the stoichiometric ratio as CaF ₂ was about 1.6 (Ca / F ₂ ≈1.6). In the calcium / magnesium removal process, exhaust gas is diffused into salt water obtained by precipitating calcium fluoride and solid-liquid separation, and by absorbing carbon dioxide in the salt water, calcium carbonate is precipitated, It was further removed by coprecipitation. In the concentration step, the salt water was concentrated with a multi-effect can to produce 15 mass% concentrated salt water. Sodium carbonate was further added to the concentrated salt water to precipitate calcium carbonate, and calcium fluoride was coprecipitated and further removed. The calcium concentration of the concentrated brine subjected to the removal treatment of calcium carbonate and calcium fluoride was about 1 mg / L. Furthermore, by-product salt was obtained by crystallizing the concentrated salt water from which calcium was removed in the crystallization step. The fluorine concentration of the 10 mass% aqueous solution of by-product salt was 0.5 mg / L. It was confirmed that the concentration of fluorine contained in the by-product salt was extremely small, impurities could be extremely small, and it could be effectively used as an industrial salt.

As shown in Examples 2 to 4, by adding calcium chloride so that the stoichiometric ratio (Ca / F ₂ ) as CaF ₂ becomes 1 or more times in the mixed washing water in the fluorine removal step, It was confirmed that the fluorine ions in the mixed washing water can be sufficiently removed, the fluorine concentration contained in the by-product salt can be reduced to reduce impurities, and a by-product salt that can be effectively used as an industrial salt can be obtained.

DESCRIPTION OF SYMBOLS 1 Processing apparatus 20 Compression apparatus 40 Supply apparatus 50 Gasification melting furnace (vertical gasification melting furnace)
52 Pyrolysis section 53 Gas reforming section 54 Melting section 80 Gas purification device 90 Washing water treatment device

Claims (6)

In the fluorine-containing waste disposal method of detoxifying the fluorine-containing liquid waste by a vertical gasification melting furnace and gasifying other waste and recovering it as fuel gas,
A compression step of batch-compressing the other waste to form a compression block;
Fluorine-containing liquid waste is supplied to the thermal decomposition section of the vertical gasification and melting furnace together with the compression block to thermally decompose and gasify, and the generated gas is gas-reformed in the gas reforming section of the vertical gasification and melting furnace. A gasification and melting step of melting and discharging incombustibles in the melting section of the vertical gasification and melting furnace,
A gas refining process in which the reformed gas that has been gas reformed is purified by washing with cleaning water and recovered as fuel gas;
A treatment method for fluorine-containing waste, comprising: a washing water treatment step for removing fluorine from the washing water obtained by washing the reformed gas in the gas purification step. In the fluorine-containing waste disposal method of detoxifying fluorine-containing solid waste by a vertical gasification melting furnace and gasifying other waste and recovering it as fuel gas,
A compression step of batch-compressing a mixture of fluorine-containing solid waste and the other waste to form a mixture compression block;
The mixture compression block is supplied to the pyrolysis section of the vertical gasification and melting furnace to be pyrolyzed and gasified, and the generated gas is gas reformed in the gas reforming section of the vertical gasification and melting furnace, and the incombustible material is A gasification and melting step of melting and discharging in the melting section of the vertical gasification melting furnace;
A gas refining process in which the reformed gas that has been gas reformed is purified by washing with cleaning water and recovered as fuel gas;
A treatment method for fluorine-containing waste, comprising: a washing water treatment step for removing fluorine from the washing water obtained by washing the reformed gas in the gas purification step. The method for treating a fluorine-containing waste according to claim 1 or 2, wherein the washing water treatment step comprises adding calcium compounds to the washing water to precipitate and separate calcium fluoride to remove fluorine. Includes the SiO ₂ in the washing water, washing water treatment step, fluorine-containing according to claim 1 or 2, to remove the fluorine precipitated separated potassium silicofluoride was added potassium compound to the wash water Waste disposal method. In a fluorine-containing waste treatment device that detoxifies fluorine-containing liquid waste and gasifies other waste and collects it as fuel gas,
A compression apparatus for batch-compressing the other waste and forming a compression block;
Vertical gasification melting furnace having a pyrolysis section, a gas reforming section and a melting section;
A supply device for supplying the compression block and fluorine-containing liquid waste to the pyrolysis section;
A gas purification device for purifying the gas reformed by the gas reforming unit with washing water and purifying it, and collecting it as fuel gas;
A cleaning water treatment device for removing fluorine from the cleaning water in which the reformed gas is cleaned by a gas purification device,
The pyrolysis section of the vertical gasification melting furnace pyrolyzes and gasifies the compression block and the fluorine-containing liquid waste, the gas reforming section gas reforms the generated gas, and the melting section is the compression block. And a fluorine-containing waste disposal apparatus characterized by melting and discharging incombustibles of fluorine-containing liquid waste. In a fluorine-containing waste treatment device that detoxifies fluorine-containing solid waste and gasifies other waste and collects it as fuel gas,
A compression device for batch-compressing a mixture of fluorine-containing solid waste and the other waste and forming a mixture compression block;
Vertical gasification melting furnace having a pyrolysis section, a gas reforming section and a melting section;
A supply device for supplying the mixture compression block to the thermal decomposition section of the vertical gasification melting furnace;
A gas purification device for purifying the gas reformed by the gas reforming unit with washing water and purifying it, and collecting it as fuel gas;
A cleaning water treatment device for removing fluorine from the cleaning water in which the reformed gas is cleaned by a gas purification device,
The pyrolysis section of the vertical gasification melting furnace pyrolyzes and gasifies the mixture compression block, the gas reforming section gas reforms the generated gas, and the melting section melts the incombustible material of the mixture compression block. An apparatus for treating fluorine-containing waste, characterized by being discharged.

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