JP2006205156A - Method of manufacturing high-quality aggregate from incinerated ash produced by circulating flow furnace - Google Patents

Abstract

<P>PROBLEM TO BE SOLVED: To provide a system for manufacturing high-quality aggregate high in crystallinity, facilitating base adjustment of incinerated ash for manufacturing aggregate by incinerating waste and fusing incinerated ash and enabling stable operation of an ash fusing furnace and low in consumption of assistant fuel. <P>SOLUTION: In a system for fusing incinerated ash having a crystallizing conveyor 25 which crystallizes aggregate while cooling after fusing the incinerated ash of waste incinerated in a circulating flow furnace 6 in an ash fusing furnace 22, the circulating flow furnace 6 is supplied with lime stone together with waste so that the lime stone is excessive in desulfurization and desalt in the furnace. The system for fusing the incinerated ash comprises a step for generating thermal decomposition reaction which makes the lime stone to be CaO in high temperature, a step for injecting the incinerated ash evenly mixed with surplus lime content into the ash fusing furnace 22, and a step for manufacturing high-quality aggregate by cooling a fused slug with the crystallizing conveyor 25 without re-heating, and the supply volume of the lime stone is set so that the basicity (CaO/SiO<SB>2</SB>ratio) of the incinerated ash to be injected into the ash fusing furnace 22 may be in the range of 0.15-2.5. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

  The present invention is produced from a circulating fluidized furnace that incinerates solid carbonaceous waste such as sewage sludge, municipal waste, industrial waste, coal, etc., and produces aggregates etc. by melting ash generated by incineration. The present invention relates to a method for producing high-quality aggregate from incinerated ash.

  Conventionally, as an incineration treatment system for sewage sludge, municipal waste, industrial waste, etc., these wastes are incinerated in a bubble-type fluidized furnace, and the incinerated ash is melted in an ash melting furnace to form slag to create road aggregate and other construction aggregates A system for manufacturing is widely used.

The bubble-type fluidized furnace used in such a system is particularly suitable for burning wastes with a high water content such as sludge because of the large heat capacity of the fluidized sand and the uniform temperature due to stirring. Incinerated ash generated by incineration in a bubble fluidized furnace is melted in an ash melting furnace, cooled and solidified to form slag, which is used as a building aggregate, etc., in order to lower the melting temperature of ash A melting aid is supplied to the ash melting furnace together with ash to adjust the basicity (CaO / SiO ₂ ratio). The slag is improved in quality and strength by generating and growing crystal nuclei in the slag by temperature-controlled reheating.

An example of such a waste incineration and aggregate production system using a bubble-type fluidized furnace and an ash melting furnace will be described with reference to FIG.
In FIG. 5, the system includes a pressure-feed pump 32 that supplies waste 31 to the bubble-type fluidized furnace 36, a blower 43 that supplies air to the bubble-type fluidized furnace 36, an air preheater 37 that preheats the air, and white smoke prevention. 38, gas cooling tower 39, bag filter 40, induction fan 41, white smoke prevention fan 44, flue gas treatment tower 42, ash hopper 45 for storing fly ash collected by the bag filter 40, ash melting furnace A side hopper 49, a feeder 50 for supplying ash and melting aid to the ash melting furnace 53, a gas cooling tower 55, a slag crystallization conveyor 56, a slag heating burner 57, and the like.

  For example, the organic waste (dehydrated cake) 31 is stably and continuously supplied to the bubble-type fluidized furnace 36 by the pressure feed pump 32, and is substantially uniformly stirred and mixed in the fluidized bed 61, dried, pyrolyzed, partially burned, and freeboard. At 62, unburned gas burns. The combustion exhaust gas leaves the free board 62 and is recovered by heating the air sent from the fluid air blower 43 to about 650 ° C. by the air preheater 37, and the heated air is heated by the fluidized bed 61. And blown in as combustion air. The flue gas discharged from the air preheater 37 is further cooled to about 300 ° C. by the air sent from the white smoke preventer fan 44 by the white smoke preventer 38, and the incineration ash is collected and removed by the bag filter 40. Thereafter, the combustion exhaust gas is discharged after the acid gas (SOx, HCl) is removed in the smoke treatment tower 42.

  The incinerated ash collected by the bag filter 40 is stored in the ash hopper 45 and then supplied in a fixed amount to the ash melting furnace side hopper 49 by the ash transporter 46. A melting aid for lowering the ash melting temperature is quantitatively supplied to the ash melting furnace-side hopper 49 by a melting aid supplier 48 below the melting aid hopper 47. The incinerated ash and the melting aid supplied in a fixed amount to the ash melting furnace side hopper 49 are supplied in a fixed amount to the ash melting furnace 53 through a fixed supply device 50 and are heated to a high temperature of 1400 to 1700 ° C. by combustion gas ejected from the combustion nozzle 52. The incinerated ash is melted almost instantaneously in the furnace held in the field, and the molten incinerated ash is discharged from the lower part of the furnace and is cooled and solidified to become slag. The combustion gas in the ash melting furnace 53 is completely burned with unburned fuel by secondary combustion in the secondary combustion chamber 54 at the upper part of the furnace, and cooled to about 300 ° C. in the gas cooling tower 55, and then the bubble-type fluidized furnace. The ash is collected and removed by the bag filter 40 and the acid gas (SOx, HCl) is removed by the flue gas treatment tower 42 and discharged.

  The slag is crystallized by being subjected to temperature control such as reheating (700 ° C. 1 h + 900 ° C. 1 h) by a heating burner 59 while being conveyed on the crystallization conveyor 56, and becomes a high-quality aggregate 60. The burner combustion exhaust gas is introduced into the gas cooling tower 55, and the exhaust gas exiting the cooling tower 55 merges with the exhaust gas exiting the cooling tower 39 and is introduced into the bag filter 40.

However, in the system as described above, it is difficult to properly adjust the basicity (CaO / SiO ₂ ratio) by mixing the melting auxiliaries with the incinerated ash, and furthermore, the time responsiveness is slow. In general, the ash melting furnace is operated so that the furnace temperature exceeds the melting point by 150 to 200 ° C. Further, the melting aid, that is, limestone is used as a basicity adjusting agent (CaCO ₃₎ is less expensive than quicklime (CaO), during the reaction CaCO ₃ becomes CaO at high temperatures _{(CaCO 3 → CaO + CO 2} ) Carbon dioxide is generated to cause combustion inhibition, and the furnace temperature tends to be unstable. Further, in order to crystallize the slag into a crystalline slag having a high strength, it is necessary to reduce the cooling rate, and in order to adjust the cooling rate, a burner for reheating the slag is necessary.

  The present invention has been made in view of the above-described problems, and is easy to adjust the basicity of incineration ash, can stably operate an ash melting furnace, has low fuel consumption, and is obtained by melting incineration ash. It is an object of the present invention to provide a method for producing high-quality aggregates by incineration of waste without strict temperature control in order to make high-strength crystalline slag.

In order to achieve the above object, the present invention provides a crystallization method in which incineration ash of waste incinerated in a circulating fluidized furnace is captured from exhaust gas and melted in an ash melting furnace, and then the molten slag is crystallized while cooling. In incineration ash melting system with conveyor,
The limestone (CaCO ₃ ) is supplied to the circulating fluidized furnace together with the waste so as to become surplus in the desulfurization / desalination in the circulating fluidized furnace, and the limestone (CaCO ₃ ) causes a thermal decomposition reaction to become CaO at a high temperature. 1 step,
A second step of obtaining molten slag by capturing the incinerated ash mixed with surplus lime used for in-furnace desulfurization of the circulating fluidized furnace from the exhaust gas and introducing it into the ash melting furnace;
It comprises a third step of producing a high-quality aggregate by gradually cooling the molten slag obtained in the ash melting furnace,
The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 0.15 to 2.5. To do.
As a result, the ash melting furnace can be operated without introducing a melting auxiliary agent, and can be operated using limestone (CaCO ₃ ) which is cheaper than quick lime (CaO).
For the Matahai melting furnace without introducing limestone (CaCO _3), the reaction CaCO ₃ becomes CaO at high temperatures _{(CaCO 3 → CaO + CO 2} ) during carbon dioxide without eliciting Surui combustion inhibition occurs, the furnace The internal temperature is stable.

In claim 2, the first step is a step of continuously supplying a dehydrated cake and limestone (CaCO ₃ ) to the circulating fluidized furnace 6 to cause a thermal decomposition reaction in which the limestone (CaCO ₃ ) becomes CaO at a high temperature. There is.
In order to continuously supply dehydrated cake and limestone (CaCO ₃ ) to the circulating fluidized furnace, the composition of the incineration ash in the combustion exhaust gas mixed and stirred in the fluidized bed of the circulating fluidized furnace and discharged from the freeboard of the fluidized furnace is uniform. It becomes.

According to a third aspect of the present invention, the third step is a step of producing a high-quality aggregate by gradually cooling the molten slag obtained in the ash melting furnace with the crystallization conveyor having a heat insulating structure. .
Since it has a heat insulating structure, it is possible to produce a high-quality aggregate with a high degree of crystallinity without requiring strict temperature control.

In Claim 4, the supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace falls within the range of 0.45 to 2.5. It is characterized by that.
This enables stable operation of the melting furnace while keeping the ash melting temperature low.

When the third step is a step of producing a high-quality aggregate by slowly cooling the molten slag obtained in the ash melting furnace without reheating,
The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 1.2 to 2.5. To do.
Thus, according to the present invention, the combustion in the ash melting furnace can be stabilized by supplying the limestone together with the waste to the circulating fluidized furnace, so that the ash basicity is as high as 1.2 to 2.5 and the ash is melted. Even when the temperature is high, it is effective in that the system can be operated stably.

When the third step is a step of producing a high-quality aggregate by slowly cooling the molten slag obtained in the ash melting furnace without reheating,
The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 0.88 to 1.2. To do.
This enables stable operation of the melting furnace while keeping the ash melting temperature low, and there is no need to reheat the slag with strict temperature control, and high quality bone with high crystallinity and high strength by simple cooling. The material can be manufactured. Furthermore, the fuel consumption for the smelting furnace can be greatly reduced as the auxiliary fuel in the ash melting furnace is reduced and the fuel for reheating the slag becomes unnecessary.

In the invention of claim 7, after the combustion exhaust gas obtained from the ash melting furnace is subjected to secondary combustion, it is merged with the exhaust gas from the circulating fluidized furnace, and surplus limestone (CaCO ₃ ) during the desulfurization in the furnace is pyrolyzed. It has the 4th step in which secondary desulfurization is performed with CaO produced | generated by this and water, It is characterized by the above-mentioned.
In the invention of claim 8, when the incineration ash charged into the ash melting furnace is a three-component system of CaO—SiO ₂ —Al ₂ O ₃ , the basicity of the incineration ash (CaO / SiO ₂ ratio) ) the weight ratio between and CaO and _Al 2 _{O 3} with 0.88 to 2.5 (%) of _{(CaO: Al 2 O 3 =} 60~90: in so that 40 to 10), the limestone (CaCO ₃ ) The supply amount is set.
In this invention, when the incinerated ash charged into the ash melting furnace is a ternary system of CaO—SiO ₂ —Al ₂ O ₃ , the degree of crystallinity is as long as the cooling rate is below a certain level regardless of reheating. high.

According to this invention, limestone is supplied to the circulating fluidized furnace so as to be surplus in the desulfurization / desalting of the circulating fluidized furnace, and the thermal decomposition reaction of the limestone (CaCO ₃ ) into CaO at a high temperature is performed. And setting the supply amount of the limestone (CaCO ₃ ) so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash at the time of charging the ash melting furnace falls within the range of 0.15 to 2.5. Propose. That is, the limestone supplied to the circulating fluidized furnace together with the waste is supplied to the circulating fluidized furnace so that the limestone (CaCO ₃ ) becomes a high temperature so as to become surplus in the desulfurization / desalination in the circulating fluidized furnace. in the allowed to cause thermal decomposition reaction to be CaO, not to elicit combustion inhibition CaCO ₃ in ash melting furnace side reactions become CaO at high temperatures _{(CaCO 3 → CaO + CO 2} ) at the carbon dioxide is generated.
In this case, when the basicity (CaO / SiO ₂ ratio) of the incinerated ash is adjusted to be 0.45 to 0.88, the melting temperature in the ash melting furnace can be lowered, and the basicity (CaO / SiO _2). If the ratio is adjusted to 0.88 to 1.2, the melting temperature in the ash melting furnace can be lowered, and a high-quality aggregate with a high degree of crystallinity can be produced without requiring strict temperature control. that we can further to produce a basicity (CaO / SiO ₂ ratio) of high crystallinity high quality aggregate without requiring strict temperature control when adjusted to be from 0.88 to 2.5 Can do.

When limestone (CaCO ₃ ) is introduced into the circulating fluidized furnace together with the waste, they are stirred and mixed in the fluidized bed of the circulating fluidized furnace, and the composition of the incinerated ash in the combustion exhaust gas discharged from the freeboard of the fluidized furnace is made uniform. Is done. And since the reaction CaCO ₃ becomes CaO at high temperatures _{(CaCO 3 → CaO + CO 2} ) occurs in the circulating fluidized furnace, ash melting furnace thereby enabling stable operation.

The melting temperature of the inorganic content in the waste, that is, the ash content is determined by the composition of the ash content, particularly the basicity (CaO / SiO ₂ ratio). For example, in the case of a CaO—SiO ₂ binary system, as shown in FIG. There is a relationship. According to FIG. 2, the melting temperature is a minimum at basicity of about 0.45 and 1.2, and is slightly higher between 0.45 and 1.2, but overall the melting temperature is low during this period. .

Furthermore, the inventors obtained the test results shown in FIG. 3 for crystallization of a three-component system of CaO—SiO ₂ —Al ₂ O ₃ . In the figure, the shaded component region becomes an anorthite region with good crystallization (the incineration ash has a basicity (CaO / SiO ₂ ratio) of 0.88 to 2.5 and CaO and Al ₂ O). _{3 in} which the weight ratio (%) to ₃ is (CaO: Al ₂ O ₃ = 60 to 90:40 to 10). Common polymeric dehydrated cake, when desulfurizing a desulfurizing agent (CaCO _3), and desulfurizing agent the properties of the ash in the case of increasing (CaCO _3), respectively as T1, T2, T3, shown in Table 1 .

In Table 1, the basicity (CaO / SiO ₂ ) determined with CaO + SiO ₂ as 100% is shown in the bottom column. In FIG. 3, the percentages of CaO, SiO ₂ and Al ₂ O ₃ are plotted as T1, T2 and T3 when CaO + SiO ₂ + Al ₂ O ₃ is 100%. T3 is in the ananosite region, but T1 and T2 are outside the ananosite region.

In FIG. 3, a line with a constant basicity (CaO / SiO ₂ ) is a straight line passing through a point where CaO is 0% and Al ₂ O ₃ is 100%. Good anorthite region crystallization the weight ratio of CaO and _Al 2 _{O 3} and in the range of basicity 0 · 88 to 2.5 (%) of _{(CaO: Al 2 O 3 =} 60~90: 40 To 10). FIG. 4 shows the relationship between the cooling rate and the crystallinity of the slag in the case of T1 and T3. In the case of T1 (basicity 0.15), the degree of crystallinity decreases as the cooling rate increases, but in the case of T3 (basicity 1.0), the cooling rate is somewhat constant regardless of whether reheating is performed or not. The crystallinity is high if below.

On the other hand, when the basicity (CaO / SiO ₂ ratio) exceeds about 1.2 as shown in FIG. 2 showing the relationship between the mixing ratio and the melting point in the binary system (CaO—SiO ₂ ), the melting temperature of ash Get higher. Therefore, if the basicity of the ash is within 0.88 to 1.2, the melting temperature of the ash is low, the crystallization can be reheated, and the cooling rate can be improved without extremely slowing down. When the basicity is 1.2 to 2.5, the melting temperature becomes high, but the crystallization can be improved without reheating and controlling the temperature. According to the present invention, the combustion in the ash melting furnace can be stabilized by supplying the limestone together with the waste to the circulating fluidized furnace, so the ash basicity is as high as 1.2 to 2.5 and the ash melting temperature is high. Even if it is high, it is effective in that the system can be operated stably.

  The present invention is implemented in the form as described above, and has the effects described below.

By introducing limestone (CaCO ₃ ) together with waste into the circulating fluidized furnace, the composition of the incinerated ash becomes uniform, and the ash melting furnace can be stably operated.

Circulating fluidized furnace so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash falls within the range of 0.15 to 2.5, preferably 0.45 to 2.5, and more preferably 0.88 to 2.5. By putting limestone (CaCO ₃ ) together with waste, stable operation of the melting furnace is possible while keeping the ash melting temperature low, and there is no need to reheat the slag with strict temperature control. Can produce high quality aggregates with high crystallinity and high strength. Furthermore, the fuel consumption for the smelting furnace can be greatly reduced as the auxiliary fuel in the ash melting furnace is reduced and the fuel for reheating the slag becomes unnecessary.

Waste in the circulating fluidized furnace so that the basicity of the incinerated ash (CaO / SiO ₂ ratio) falls within the range of 0.15 to 2.5, preferably 0.45 to 2.5, especially 1.2 to 2.5. In addition, by introducing limestone (CaCO ₃ ), it is possible to improve the quality of the molten slag, and there is no need to reheat the slag with strict temperature control, and the crystallization conveyor having the heat insulating structure is reheated. It is possible to produce a high-quality aggregate with a high degree of crystallinity and high strength by cooling (slow cooling).

  Hereinafter, exemplary embodiments of the present invention will be described in detail with reference to the drawings. However, the dimensions, materials, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the present invention unless otherwise specified, but are merely illustrative examples. Not too much.

  FIG. 1 shows the configuration of an incineration ash basicity adjustment system using a circulating fluidized furnace according to an embodiment of the present invention. The system includes an organic waste (dehydrated cake) 1 charged into the hopper 1 and a pressure pump 2 for pumping the melting aid 28, a circulating fluidizing furnace 6, a hot cyclone 7, an air preheater 8, a white smoke preventer 9, and a gas. Waste incineration system comprising cooling tower 10, bag filter 11, induction fan 12, chimney 13, fluid air blower 14, white smoke prevention fan 15, ash hopper 16, etc., ash melting furnace side ash hopper 18, ash metering machine 19, an incineration ash melting system including an ash melting furnace 22, a secondary combustion chamber 23, a gas cooling tower 24, a crystallization conveyor 25, and the like.

An organic waste (dehydrated cake) 1 and a limestone (CaCO ₃ ) 28 as a melting aid are continuously supplied to a circulating fluidized furnace 6 by a pressure pump 2 and dried and thermally decomposed in a sand layer 29 of the fluidized furnace 6. Then, the unburned gas is burned in the free board 30 after partial combustion. In the furnace, desulfurization and desalting are performed by limestone (CaCO ₃ ) 28 supplied together with the organic waste (dehydrated cake) 1. The combustion exhaust gas discharged from the free board 30 and the fluidized sand are separated from the fluidized sand by the hot cyclone 7, and the separated high-temperature exhaust gas passes through the air preheater 8 and flows into the fluidized and combusted air in the fluidized bed 29. After the temperature is raised to about 650 ° C., the temperature of the air is further raised by the white smoke preventer 9 and cooled to about 300 ° C. by the gas cooling tower 10, and the incineration ash in the exhaust gas is collected and removed by the bag filter 11. After that, it is discharged through the chimney 13.

  The incinerated ash collected by the bag filter 11 is stored in the ash hopper 16 and then supplied to the ash melting side ash hopper 18 by the ash transporter 17. The incinerated ash is uniformly mixed with the lime used for in-furnace desulfurization. The incineration ash in the ash melting side ash hopper 18 is quantitatively supplied to the ash melting furnace 22 by the ash quantitative supply device 19 through the ash supply nozzle 20 and is burned by the auxiliary fuel 26 supplied from the combustion nozzle 21 to 1400. It is melted almost instantaneously in a furnace maintained in a high temperature field of 1700 ° C. The molten slag is discharged from the lower part of the furnace, and the combustion exhaust gas is discharged from the upper part of the furnace to the secondary combustion chamber 23 and is completely burned by the secondary combustion. The combustion gas is cooled to about 200 ° C. in the gas cooling tower 24, and then merged with the exhaust gas from the white smoke preventer 9 and introduced into the gas cooling tower 10.

In the gas cooling tower 10, water is sprayed from the bottom, and quick lime (CaO) generated by thermal decomposition of excess limestone (CaCO ₃ ) during desulfurization in the furnace and water are sulfite generation reaction and slaked lime generation reaction. As a result, secondary desulfurization is performed. The molten slag is gradually cooled by a crystallization conveyor 25 having a heat insulating structure, and is taken out as a high-quality aggregate 27 having a high degree of crystallinity. At the time of this crystallization, the conventional temperature control by the reburning burner is unnecessary. Note that water vapor generated in the crystallization conveyor 25 is attracted to the gas cooling tower 24.

  According to the present invention, the basicity of the incineration ash is easily adjusted, the ash melting furnace can be stably operated, the amount of fuel consumption is small, and the slag obtained by melting the incineration ash is converted into a high-strength crystalline slag. Therefore, it is possible to produce high quality aggregates by incinerating waste without the need for reheating slag with strict temperature control.

It is a figure which shows the structure of the incineration ash basicity adjustment system by the circulation flow furnace concerning embodiment of this invention. It is a diagram showing the relationship between the mixing ratio and the melting point in CaO-SiO ₂ two-component system. _CaO-SiO 2 _-Al 2 component ratio of the ternary system of _{O 3} and is a diagram showing the relationship of the crystallization region. It is a figure which shows the relationship between the slow cooling rate of slag, and a crystallinity degree. It is an example of the waste incineration and aggregate production system which used the conventional bubble type | mold flow furnace and the ash melting furnace.

Explanation of symbols

DESCRIPTION OF SYMBOLS 1 Dewatering cake 2 Pressure pump 6 Circulating flow furnace 7 Hot cyclone 8 Air preheater 10 Gas cooling tower 11 Bag filter 16 Ash hopper 17 Ash transport machine 18 Ash melting furnace side ash hopper 19 Ash fixed quantity supply 22 Ash melting furnace 23 Secondary Combustion chamber 24 Gas cooling tower 25 Crystallization conveyor 27 High quality aggregate 28 Melting aid

Claims (8)

Incineration ash melting system having a crystallization conveyor that captures incineration ash of waste incinerated in a circulating fluidized furnace from the exhaust gas and melts it in an ash melting furnace, and then crystallizes while cooling the molten slag,
The limestone (CaCO ₃ ) is supplied to the circulating fluidized furnace together with the waste so as to become surplus in the desulfurization / desalination in the circulating fluidized furnace, and the limestone (CaCO ₃ ) causes a thermal decomposition reaction to become CaO at a high temperature. 1 step,
A second step of obtaining molten slag by capturing the incinerated ash mixed with surplus lime used for in-furnace desulfurization of the circulating fluidized furnace from the exhaust gas and introducing it into the ash melting furnace;
It comprises a third step of producing a high-quality aggregate by gradually cooling the molten slag obtained in the ash melting furnace,
The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 0.15 to 2.5. A method for producing high-quality aggregate from incinerated ash generated from a circulating fluidizing furnace. The first step is a step of continuously supplying a dehydrated cake and limestone (CaCO ₃ ) to a circulating flow furnace to cause a thermal decomposition reaction in which the limestone (CaCO ₃ ) becomes CaO at a high temperature. A method for producing high-quality aggregates from incinerated ash generated from a circulating fluidized furnace.   The third step is a step of producing a high-quality aggregate by slowly cooling the molten slag obtained in the ash melting furnace with the crystallization conveyor having a heat insulating structure. To produce high quality aggregates from incinerated ash. The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 0.45 to 2.5. A method for producing high-quality aggregate from incinerated ash generated from the circulating fluidized furnace according to claim 1. In the case where the third step is a step of producing a high quality aggregate by slowly cooling the molten slag obtained in the ash melting furnace without reheating,
The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 1.2 to 2.5. A method for producing high-quality aggregate from incinerated ash generated from the circulating fluidized furnace according to claim 1. In the case where the third step is a step of producing a high quality aggregate by slowly cooling the molten slag obtained in the ash melting furnace without reheating,
The supply amount of the limestone (CaCO ₃ ) is set so that the basicity (CaO / SiO ₂ ratio) of the incinerated ash charged into the ash melting furnace is in the range of 0.88 to 1.2. A method for producing high-quality aggregate from incinerated ash generated from the circulating fluidized furnace according to claim 1. Combustion exhaust gas obtained from the ash melting furnace is combined with exhaust gas from a circulating fluidized furnace after secondary combustion, and excess limestone (CaCO ₃ ) at the time of desulfurization in the furnace is thermally decomposed to generate CaO A method for producing high-quality aggregate from incinerated ash generated from a circulating fluidized furnace according to claim 1, further comprising a fourth step in which secondary desulfurization is performed with water. When the incineration ash charged into the ash melting furnace is a ternary system of CaO—SiO ₂ —Al ₂ O ₃ , the basicity (CaO / SiO ₂ ratio) of the incineration ash is 0.88 to 2.5. in and CaO and _Al 2 _{O 3} and the weight ratio (%) of _{(CaO: Al 2 O 3 =} 60~90: 40~10) to the made to, setting the supply amount of the limestone (CaCO ₃₎ A method for producing high-quality aggregate from incinerated ash generated from the circulating fluidized furnace according to claim 1.

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