WO1992001771A1 - Method of turning wastes into solid body and method of burning such solid body - Google Patents

Method of turning wastes into solid body and method of burning such solid body Download PDF

Info

Publication number
WO1992001771A1
WO1992001771A1 PCT/JP1991/000961 JP9100961W WO9201771A1 WO 1992001771 A1 WO1992001771 A1 WO 1992001771A1 JP 9100961 W JP9100961 W JP 9100961W WO 9201771 A1 WO9201771 A1 WO 9201771A1
Authority
WO
WIPO (PCT)
Prior art keywords
waste
crusher
reactor
earth metal
metal oxide
Prior art date
Application number
PCT/JP1991/000961
Other languages
French (fr)
Japanese (ja)
Inventor
Muneo Azegami
Shozo Suzuki
Original Assignee
Prand Research Institute
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority claimed from JP2193798A external-priority patent/JP2954990B2/en
Priority claimed from JP2401438A external-priority patent/JPH04210284A/en
Priority claimed from JP3032760A external-priority patent/JP2798189B2/en
Priority claimed from JP3071221A external-priority patent/JP3067827B2/en
Application filed by Prand Research Institute filed Critical Prand Research Institute
Publication of WO1992001771A1 publication Critical patent/WO1992001771A1/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/48Solid fuels essentially based on materials of non-mineral origin on industrial residues and waste materials
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Definitions

  • the present invention targets flammable waste that has been treated and disposed of in a conventional municipal solid waste incinerator, by subjecting it to a physical and chemical reaction treatment to produce solids that can be used as recycled resources (hereinafter referred to as the product).
  • the product is used as a hybrid fuel suitable for the purpose by directly using the product as it is and mixing it with a solid fuel such as coal as appropriate.
  • the present invention also relates to an incineration method in which the solids are put into an incinerator and incinerated.
  • incineration technology is intended to uniformly burn chemicals such as plastics in waste, so that conventional incineration technology will be improved to a more advanced combustion technology, for example, by introducing a fluidization method. Became.
  • new technologies are being developed for exhaust gas treatment, such as measures against NOx and the removal of harmful chemicals such as dioxins.
  • the second reason is that the organic matter contained in combustible waste is biologically unstable, and when used as fuel, emits offensive odors, generates methane gas, breaks down products, etc. This had a negative effect on the environment inside and outside the factory, and caused trouble in the transport and storage operations. In addition, methane gas caused fire and explosion accidents.
  • the fuel is used alone, and when used alone as a fuel, the boiler has a negative effect of lowering the efficiency.
  • the first object of the present invention is to improve the conventional waste disposal method that relied on incineration and landfill, and to convert so-called combustible waste into substances that can be used as recycled resources
  • the present invention provides a method for producing solids from waste, which solves the above-mentioned difficult reasons that have been faced in the field of ⁇ fuel conversion '', in which natural fuels can be used as substitutes.
  • a second object of the present invention is to chemically and physically treat perishable organic substances, mainly carbohydrates, proteins, fats, etc., contained in waste with additives such as alkaline earth metal oxides.
  • Another object of the present invention is to provide a method for producing a solid fuel that can be converted into a biologically stable substance, thereby enabling long-term storage and stable combustion.
  • a third object of the present invention is to provide a method for producing the hybrid fuel by mixing the resulting "products" alone or in combination with coal, and mixing with other natural fuels. It is to provide.
  • a fourth object of the present invention is to provide a waste pre-treatment step to carry out the chemical reaction and physical operation according to the present invention in order to improve the existing incineration technology from the aspect of environmental protection. the by modifying, plant sanitation in storage process of the waste, with dripping also the effect of prevention of odor-causing, at C a 0 2 effects of Al force Li earth metals, such as added in the combustion process It is an object of the present invention to provide a method for incinerating solids that has the effect of cleaning exhaust gas.
  • the waste such as municipal waste is put into a waste receiving tank, it is solidified by a dry neutralization reactor through a first crusher, a second crusher, and a mixed distillation reactor.
  • a dry neutralization reactor After the waste such as municipal waste is put into a waste receiving tank, it is solidified by a dry neutralization reactor through a first crusher, a second crusher, and a mixed distillation reactor.
  • the addition amount of the alkaline earth metal oxide according to the characteristics of the waste is added to rationalize physical and chemical
  • This is a method for producing solids from waste, which is characterized by conducting a reaction treatment. .
  • the waste receiving tank or the first crusher is added with 0 to 30% of the total amount of the alkaline earth metal oxide added to the waste.
  • Physical and chemical reaction treatment, or in the second crusher physical and chemical reaction treatment by adding 0 to 50% of the total addition amount of alkaline earth metal oxide to the waste.
  • a physical and chemical reaction treatment is performed by adding 2 to 100% of the total amount of the alkaline earth metal oxide to the waste.
  • the total amount of the alkaline earth metal oxide is added at an appropriate ratio in a plurality of locations of the waste receiving tank, the first crusher, the second crusher, and the mixed storage reactor. It is desirable to perform physical and chemical reaction treatment.
  • the value of K is in the range of 0.2 to 1.2.
  • the waste receiving tank, the first crusher, the second crusher, the mixed storage reactor, and the dry neutralization reactor pass through the waste receiving tank, the first crusher, the second crusher, and the like from the municipal waste.
  • an appropriate alkaline earth metal oxide to one or more of the crusher, the second crusher, and the mixed storage reactor, and performing a physical and chemical reaction treatment, It is possible to obtain solids that are effective as fuels and materials for civil engineering and construction materials.
  • the alkaline earth metal oxide added in each of the above processes can reduce 11% of organic matter by analyzing and measuring water, plastics, inorganic substances, and resource substances that constitute waste such as municipal solid waste. It is possible to calculate and obtain an effective and optimum addition amount based on the percentage of the organic matter U.
  • the present invention provides a mixing and storage reactor in which an appropriate amount of an additive containing alkaline earth metal oxide is charged into a mixing and storage reactor, and the waste which has been previously crushed and from which incombustibles have been removed is added.
  • the reacted first product waste is charged into a mixed degassing reactor, and an appropriate amount of an additive containing an alkaline earth metal oxide is added as necessary, to perform the mixing reaction and
  • the reaction product gas is degassed, the reacted second product waste is put into a compression molding machine to perform compression molding, and then the compression molded third product waste is put into a dry neutralization reactor. Dry neutralization reaction, and, if necessary, sieving with a sieving machine to obtain solid fuel.
  • the reaction in the mixed storage reactor is performed in a closed state, at a temperature of 60 to 100 and at a temperature of not more than 1 hour, and the reaction in the mixed deaeration reactor is performed in an exhausted state. It is preferable to perform at least 5 minutes at a higher temperature for at least 5 minutes.
  • the waste was coarsely crushed by a first crusher and non-combustibles were selectively removed in order to obtain finely crushed waste, and then crushed.
  • An appropriate amount of additive containing alkaline earth metal oxide is added to the waste, crushed by the second crusher, and the incombustibles contained in the composite material of the waste are separated and removed.
  • the waste is finely crushed by a third crusher, and further, the reacted first generated waste, the degassed second generated waste, or sieved by the sieve. Powder waste as needed At the same time, it is desirable to reflux only a necessary amount to the mixed storage reactor.
  • a solid material serving as a clean fuel can be obtained from waste such as refuse.
  • the resulting solids are physically, chemically and biologically stabilized and can be stored for long periods of time.
  • the present invention is a method for producing a hybrid flint, which comprises performing a compression molding process or a granulation process after mixing a natural fuel with a waste solid fuel and then subjecting the mixed fuel to a natural fuel.
  • the hybrid fuel contains waste fuel at a constant rate, and therefore can be manufactured at a lower cost than the conventional cost of 100% natural fuel.
  • solid fuel contains alkaline earth metal oxides such as Ca0, it absorbs acidic gas contained in exhaust gas, resulting in a clean fuel with no environmental pollution. can do.
  • This hybrid fuel can be used as fuel for small boilers such as simple stoves, etc., and its quality is close to that of anthracite, and it contains solid fuel from waste.
  • the quality is as effective as a binder, making it easier to granulate. It has a calorific value equivalent to that of low-grade coal, which is intermediate between solid fuels made from natural fuels and wastes, and can be sufficiently used as industrial fuels, and can be used for many uses of various fuels.
  • the present invention provides a method for manufacturing a waste container, comprising: inserting waste such as municipal solid waste into a waste receiving tank, and then charging the waste into an incinerator to incinerate the waste; It is characterized in that the physical and chemical reaction treatment is performed rationally by adding the amount according to the characteristics of the waste. Waste incineration method.
  • waste incineration method characterized by adding an amount of an alkaline earth metal oxide according to the properties of the waste to one of the two and rationally performing a physical / chemical reaction treatment.
  • waste incineration method characterized by the following:
  • the waste such as municipal waste is put into the waste receiving tank, it is put into the incinerator via the first crusher, the first sorter, the second crusher, the second sorter, and the mixed distillation reactor, and is disposed of.
  • the waste receiving tank, the first crusher, the second crusher, and the mixed storage reactor may be used as alkaline earth metal. This is a waste incineration method characterized in that an appropriate amount of oxide is added and a physicochemical reaction is performed rationally.
  • an appropriate amount of alkaline earth metal oxide is added in the processing steps up to the waste receiving tank, the first crusher, the second crusher, or the mixed storage reactor to provide physical and chemical
  • the incineration treatment can prevent corrosion due to water formation, eliminate acidic gases such as hydrogen chloride and sulfur oxides, and achieve high efficiency You can get lean energy. It can also be applied efficiently to co-firing with refuse in coal-fired plants.
  • FIG. 1 shows a conceptual process diagram for obtaining solids (fuel) from collected waste and incinerating an intermediate product according to an embodiment of the present invention.
  • FIG. 2 shows a process chart of an embodiment of a production method for producing a hybrid fuel by mixing solid fuel and natural fuel by the waste obtained in the process shown in FIG. is there.
  • FIG. 1 is a conceptual diagram showing a process for obtaining solids from collected waste and incinerating an intermediate product according to an embodiment of the present invention.
  • waste G such as garbage removed from households and offices is composed of combustible materials such as paper, cardboard and fiber, and non-combustible materials such as iron, aluminum, glass, and soil. It is composed of the water contained therein, is transported by trucks, packers, and other transport vehicles, and is once put into a waste receiving tank 1 consisting of pits and the like. From the waste receiving tank 1, only the required amount is fed into the first crusher 3 at the required time.
  • the first crusher 3 is, for example, a hydraulic low-speed driven tear crusher, and its detailed structure is omitted because its specific structure is publicly known, but it has two or three shafts whose rotation speeds are different from each other, The outer periphery of each shaft is provided with a plurality of blade forces.
  • the input waste G is gripped by a two- or three-axis rotary tearing blade with different rotational speeds, tears through, breaks through to a strong one, and is driven by a low-speed, high-torque hydraulic drive. Is slowly torn and discharged from the outlet at the bottom of the body.
  • the drive of the first crusher 3 is of a hydraulic drive type.
  • the first waste G 1 roughly crushed by the first crusher 3 is sent to a first sorter 5 composed of, for example, a belt conveyor.
  • the first separator 5 is provided with a magnetic separator, which removes metals such as iron and non-ferrous metals and harmful hazardous materials.
  • the first sorter 5 medium-sized inorganic substances such as bottles and blocks are sorted and removed.
  • the second waste G 2 is sent to the second crusher 7.
  • the second crusher 7 is made of, for example, a hammer mill. The second crusher 7 further crushes the waste G2.
  • the third waste G3 finely crushed by the second crusher 7 is sent to a second separator 9 including, for example, a separator, a sieve, a specific gravity separator, and the like.
  • a second separator 9 including, for example, a separator, a sieve, a specific gravity separator, and the like.
  • metal and inorganic substances that could not be completely removed by the first sorter 5 are removed, and the fourth waste G 4 is sent to the third crusher 11.
  • the third crusher 11 further crushes the fourth waste G4 by using, for example, a ring glider mill. However, when the required crush particle size can be obtained in the second crusher 7, the crusher may be omitted without being charged into the third crusher 11.
  • an appropriate amount of an additive containing an alkaline earth metal oxide such as Ca 0 is fed together with the second waste G 2 sorted by the first sorter 5.
  • the second waste G 2 is crushed and uniformly mixed and contacted with the alkaline earth metal oxide C a O.
  • C a (OH) 2 becomes the C a 0 is alkali earth metal oxide and water (H 2 0) included in the second waste G 2 are reacted, the C a (OH) 2 is dispersed in the solid second waste G2.
  • the input amount of the alkaline earth metal oxide Ca 0 is 2 to 5%, preferably about 3%, based on the input amount of the waste.
  • the mixed storage reactor 13 is composed of, for example, a rotary hexagonal mixer, a ribbon mixer, or a moving screw-type stirrer, and is mixed for a certain period of time while being stored.
  • the reaction rate can be increased by heating the mixed storage reactor 13 with hot air or a heating tube if necessary. It is preferable to conduct the treatment in a closed state, for example, at a temperature of 60 to 1 1 ⁇ for 1 hour or more.
  • the mixed storage reactor 13 contained the sixth waste G 6 (first generated waste) generated by the reaction and an appropriate amount of alkaline earth metal oxide C a 0 as necessary.
  • the additive material is introduced into the mixed degassing reactor 15 to perform a mixing reaction and degas ammonia and the like. That is, it is preferable to perform the heating at a temperature at least 5 or more higher than the above-mentioned temperature for 5 minutes or more under the exhaust state.
  • the reacted seventh waste G7 (second waste product) is put into a compression molding machine 17, where the density is increased by a compression action, and then extruded to be formed into granules.
  • the eighth waste G 8 (third generated waste) formed into granules by the compression molding machine 17 is supplied to the dry neutralization reactor 19.
  • the solid matter S thus obtained can be sieved with a sieve 21 as needed to be taken out as a solid fuel, or taken out as a material for civil engineering and building materials and used. Is widely applied to industry That is, the following operation occurs between the mixed storage reactor 13 and the dry neutralization reactor 19.
  • Proteins, carbohydrates, and lipids contained in organic matter are denatured by the action of heat and alkali, and some are hydrolyzed.
  • alkali and mechanical action paper, wood, plant residues, etc. are loosened in a fibrous form and bacteria are killed.
  • the granular waste thus obtained is sieved by a sieving device 21 as necessary to remove solid fuel S as a solid.c
  • powder smaller than a certain size does not have a certain size. Refluxed and recharged.
  • the sixth waste G6 mixed while being stored in the mixed storage reactor 13 is checked for quality stabilization before being fed into the mixed degassing reactor 15, and a certain If the quality has not been achieved, it is returned to the mixed storage reactor 13.
  • the ratio of this reflux depends on the reaction time and reaction conditions in the mixed distillation reactor 13, but it is sufficient to reflux up to 50%. In short, when the quality of the sixth waste G6 satisfies a certain level, it is fed into the mixed degassing reactor 15.
  • the 7th waste G7 reacted in the mixed degassing reactor 15 maintains a certain rate of reaction achievement before it is injected into the compression molding machine 17. If a certain reaction achievement rate has not been achieved after a check has been made, the mixture is returned to the mixed storage reactor 13. Therefore, only the eighth waste G8, which maintains a certain reaction achievement rate, is injected into the compression molding machine 17.
  • the sixth waste G 6 reacted in the mixed storage reactor 13 the seventh waste G 7 reacted in the mixed degassing reaction 15 or dried and neutralized in the dry neutralization reactor 19
  • the solids that have been combined and sieved in the sieve 21 are fed back many times until they reach a certain material composition, a certain reaction completion rate, and a certain size.
  • the final solid (fuel) can be taken out as a homogeneous and clean fuel.
  • an additive containing Ca 0, which is an alkaline earth metal oxide is charged in the required amount in each stage, and the chemical reaction
  • the obtained solid can be stored as fuel for a long period of time, and methane gas is not generated and gas explosion does not occur.
  • the properties of the eighth waste G8, which is an intermediate product heated and compression-molded by the compression molding machine 17, are different from those in the case of fuel production and in the case of civil engineering building material production. This can be easily selected based on the mechanical performance of the compression molding machine 17 or the replacement of parts. It is necessary to select the properties of fuel tanks for fuel tanks, such as co-firing with coal and charging into a fluidized-bed boiler and storage-force type boilers. In this example, it was confirmed that the production of a fuel particularly suitable for a fluidized-bed boiler is effective because of its low mechanical load and combustion characteristics. It is mechanically easy and effective to produce granules of approximately 5 mm to 10 mm.
  • C a 0 as an alkaline earth metal oxide is added to the waste receiving tank 1 or the first crusher 3 to the waste G such as garbage for the purpose of deodorization and control of spoilage enzyme. Physical and chemical reaction processes are performed.
  • the addition amount of Ca 0 is preferably about 0 to 30% of the total addition amount. Even if it exceeds 30%, it does not show much effect.
  • the input amount to the waste receiving tank 1 should be within the range of 10% to 20% of the total input amount.
  • C a0 is also charged together, and mixed and mixed according to the first C a0.
  • the addition of CaO is desirably performed in a physical / chemical reaction treatment by adding 0 to 50% of the total amount.
  • the purpose of feeding into the second crusher 7 is to promote uniform reaction between C a 0 and refuse in the second crusher 7 and at the same time mechanical contact between solids and solids to promote the reaction by C a O. Can be done.
  • Municipal dust generated from this type of crushing process has been biologically active, and the effects of pathogenic bacteria on the environment have been recognized to some extent.
  • the introduction of CaO into the second crusher 7 not only promotes the reaction but also has a remarkable effect on the improvement of the working environment in the factory.
  • the addition rate of C a 0 is usually 10% to 20% of the total input force; In some cases, it is appropriate to input up to 50%.
  • the mixed storage reactor 13 may be charged with the fifth waste G5 pulverized by the third crusher 11 at the same time as charging Ca0.
  • the added amount of Ca 0 is desirably 20% to 100% of the total added amount.
  • the purpose of introducing C a 0 in this step is to complete the reaction with C a O.
  • the compression-formed granular intermediate product has a temperature of 50 or more due to heating and the exothermic reaction of Ca0.
  • This is removed in the next drying step, and solidified by the reaction between calcium and carbon dioxide in the combustion gas, so that a solid that can be easily handled is obtained. This can be used as fuel as it is.
  • the lower calorific value per kilogram is close to 400 kcal, and in the example of Europe it is 350 kcal, and in any case, the coal boiler It becomes a fuel with optimal physical and chemical properties and biologically stable storage characteristics for co-firing c.
  • the above-mentioned waste G is put into the waste receiving tank 1 and then dried and neutralized Solids S are obtained through the processing steps up to the reactor 19, but the C a 0 added to the waste receiving tank 1, the first crusher 3, the second crusher 7, and the mixed storage reactor 13 is obtained.
  • the total amount is preferably determined by the following means.
  • the waste G such as municipal solid waste is set at 100%, and when analyzed, this waste G contains moisture, plastics, inorganic substances, and resources. Then, the moisture is reduced to W% using a dryer, etc.
  • the method of determining the optimal addition rate in the range of K-0.2 to 1.2 as a result of investigating the adaptability to waste quality in various countries around the world is specified.
  • the W term corrects for the effective addition of C a O to organic matter when moisture is excessive.
  • the waste receiving tank 1 or the first crusher 3 is about 1 to 2%
  • the second crusher 7 is about 2%
  • the mixed-bed storage reactor 13 it is desirable to add 1 to 5% C a 0 and to perform physical and chemical reaction treatment. In this way, by adding C a0 and physically and chemically treating in each treatment step of treating waste G, fuel or civil engineering material as a biologically stable solid S is obtained. Material can be obtained.
  • the force described using Ca 0 as a column of the alkaline earth metal oxide ⁇ The force obtained by mixing Mg 0 into Ca 0 may be used, or only Mg 0 may be used. Alternatively, C a (OH) 2 or a mixture thereof may be used.
  • Fig. 2 shows a production method in which a hybrid fuel is obtained by mixing solid fuel S from waste obtained by the above-mentioned production method and natural fuel N, which mainly uses coal.
  • solid fuel S. from waste is put into a crusher 23 and crushed to a finer particle size by the crusher 23.
  • the fine-grained solid fuel crushed by the crusher 23 is fed into a specific gravity separator 25, which further removes impurities (incombustibles) such as glass and iron scraps. Is done.
  • the granular solid fuel from which impurities have been removed by the specific gravity difference separator 25 is charged into the mixer 27, and the natural fuel N, which is mainly coal, is charged into the mixer 27. Therefore, in the mixer 27, the particulate solid fuel and the natural fuel N are mixed at a fixed rate for a fixed time.
  • the mixture subjected to the mixing treatment in the mixer 27 is, for example, charged into a compression molding machine 2 and compression-molded, and further subjected to a drying treatment under a certain condition in a dryer 31 to thereby obtain, for example, a charcoal or briquette. Haiburi head fuel H a solid consisting of size will be obtained.
  • the mixture subjected to the mixing treatment in the mixer 27 is charged into a granulator 33 in some cases.
  • Water or C a (OH) 2 is added to the granulator 33 and granulated under certain conditions. Further, by drying under a certain condition in the dryer 35, a layer of natural fuel N adheres to the outer periphery with the solid fuel S as waste as a core, and a granular material having a size of, for example, soybean is obtained. the fact that the granules hybrid fuel H B is obtained.
  • the solid hybrid fuel H A and the granulated hybrid KH B obtained in this way contain a certain percentage of solid fuel S from waste, so the conventional 100% It can be manufactured at lower cost than the cost of natural fuel N, and the acid gas generated by the combustion of sulfur and chlorine contained in natural fuel N is converted to solid fuel S from waste. It is absorbed by the reaction with the contained C a 0.
  • the solid fuel S from waste is contained at a certain ratio, and the solid fuel S contains Ca0, so that the exhaust gas is cleaned and the environment is reduced. Clean fuel without pollution Obviously, the solid fuel S from waste is contained at a certain ratio, and the solid fuel S contains Ca0, so that the exhaust gas is cleaned and the environment is reduced. Clean fuel without pollution Obviously, the solid fuel S from waste is contained at a certain ratio, and the solid fuel S contains Ca0, so that the exhaust gas is cleaned and the environment is reduced. Clean fuel without pollution Becomes
  • This hybrid fuel can be used as fuel for small boilers such as simple stoves, etc., and its quality is close to that of anthracite, and it also contains solid fuel S as waste. From this, it becomes a fiber, has an effect as a binder, and is easily granulated. It has a calorie equivalent to that of low-grade coal, which is intermediate between natural fuel ⁇ and solid fuel S made from waste, and is sufficiently usable as a fuel, and is suitable for many uses of various fuels. It can be used.
  • the above-mentioned waste G is put into the waste receiving tank 1, and the intermediate products obtained in the processing steps up to the dry neutralization reactor 19 are put into the incinerator 37 shown in Fig. 1. Can be incinerated.
  • the required amount of waste G is put into the waste receiving tank 1, and the Ca 0 is added in an appropriate amount according to the required amount and the characteristics of the waste G.
  • the refuse in the waste receiving tank 1 can be directly injected into the incinerator 37 even if incinerated. It is possible to prevent the decay of the gas and to effectively absorb the acid gas in the combustion process.
  • the second crusher 7 a suitable amount of C a0 is charged, a physical / chemical reaction treatment is performed, and the third waste G3 does not flow to the second selector 9, but is indicated by a dotted line. As shown in the figure, high efficiency and clean combustion can be achieved even if the waste is put into the direct incinerator 13 and incinerated.
  • the solid matter S obtained by the method for producing solid matter from waste according to the present invention is considered to be first effectively used as fuel. In both cases, fuel costs are reduced. Blending with natural fuels also reduces the use of natural fuels. Also, this solid

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Abstract

When turning wastes (G) into a solid body (S) through processes performed in a waste receiving pit (1), first crusher (3), first screen (5), second crusher (7), second screen (9), mixing-storing reactor (13), compression molding machine (17), and drying-neutralizing reactor (19), treatment of wastes with the application of an optimum alkaline earth metal oxide such as CaO to any one or a plurality of processes in said waste receiving pit (1), first crusher (3), second crusher (7), and mixing-storing reactor (13) enables the provision of a solid body (S) effective as a raw material of environmentally clean fuel or material for construction work. An optimum quantity of CaO to be added can be found on the basis of a quantity of organic substance (U) calculated from analysis and measurement of water content (W), a quantity of plastics (P), that of inorganic substances (M), and that of re-usable substances (W) that constitute the wastes (G) with an index of 100. Further, feed-back of an appropriate quantity of wastes having passed the mixing-storing reactor (13), mixing-deaerating reactor (15), or drying-neutralizing reactor (19) to the mixing-storing reactor (13) ensures a solid body (S) far more uniform in quality. By mixing the solid body (S) thus made from wastes with a natural fuel, an excellent hybrid fuel can be obtained. When an intermediate product obtained in the course of the above treatment of wastes into the solid body (S) is directly charged into an incinerator (37), clean burning is possible.

Description

一 1 一 明 細 書  1 1 1 Description
廃棄物による固形物の製造方法および焼却方法  Method for producing solid matter from waste and method for incineration
技術分野  Technical field
この発明は従来都市ごみ焼却炉によつて処理処分されていた可燃 性の廃棄物を対象に、 これを物理 · 化学反応処理することによって、 再生資源と して利用可能な固形物 (以下当該プロダクツという) を 製造する固形物の製造方法に関し、 加えて、 当該プロダクツをその まま直接燃料として使用する方法および石炭など固形燃料と適宜に 混合することによって、 用途に適したハイブリ ツ ド燃料として使用 する方法、 さ らに上記固形物を焼却炉に投入して焼却する焼却方法 に関する。  The present invention targets flammable waste that has been treated and disposed of in a conventional municipal solid waste incinerator, by subjecting it to a physical and chemical reaction treatment to produce solids that can be used as recycled resources (hereinafter referred to as the product). In addition, the product is used as a hybrid fuel suitable for the purpose by directly using the product as it is and mixing it with a solid fuel such as coal as appropriate. The present invention also relates to an incineration method in which the solids are put into an incinerator and incinerated.
背景技術  Background art
近年一般家庭或いは事業所などから排出される可燃性の廃棄物は、 この中にガラスびん、 空き缶をはじめ、 さまざまな無機物を混入す るばかりではなく 、 更に、 プラスチッ クなど化学物質も多種多様に 含むようになつてきた。 このため、 従来から廃棄物を処理してきた 方法の改良改善が下記のように急速に進められてきた。  In recent years, flammable waste discharged from households and offices is not only mixed with various inorganic substances such as glass bottles and empty cans, but also contains a wide variety of chemical substances such as plastics. It has come to include. For this reason, the improvement and improvement of the conventional methods for treating waste have been rapidly promoted as follows.
第一に、 焼却技術は廃棄物中のプラスチックなどの化学物質を均 —に燃焼せしめるため、 従来の焼却技術を、 例えば流動化法を導入 するなどして、 高度な燃焼技術に改良されるようになった。 これに 関連して、 排ガス処理技術も、 新たに N O X対策やダイォキシンな ど有害化学物質の除去技術の開発などが進められている。  First, incineration technology is intended to uniformly burn chemicals such as plastics in waste, so that conventional incineration technology will be improved to a more advanced combustion technology, for example, by introducing a fluidization method. Became. In connection with this, new technologies are being developed for exhaust gas treatment, such as measures against NOx and the removal of harmful chemicals such as dioxins.
第二に、 排出源からの分別収集システムや、 搬入廃棄物の破砕選 別システムの開発によって、 焼却炉の前でこれらの無機物や有害な 化学物質を除く技術も開発された。 この中で、 資源回収技術や燃焼 ガスから余熱回収技術なども著しく進歩した。  Secondly, the development of a system to separate and collect waste from sources and a system to crush and sort incoming waste has also developed technologies to remove these inorganic and harmful chemicals before incinerators. Under these circumstances, remarkable progress has been made in resource recovery technology and technology for recovering residual heat from combustion gas.
このように廃棄物処理システムが技術的に高度なものとなるにつ れて、 廃棄物処理のために支払われる社会的費用が著しく増大し、 地方公共団体における財政的な負担が大きな問題となつてきた。 そ の上、 最近では地球谭境の保全対策に一貫する課題に関連して、 焼 却炉から排出される c o 9 を抑制する必要が生じ、 これまで 「焼却」 と 「埋立」 に頼ってきた可燃性廃棄物処理の処理方法を根本から造 り変えていく必要に迫られるようになった。 As the waste management system becomes more technically advanced, the social costs paid for waste management increase significantly, and the financial burden on local governments becomes a major problem. Have been. So Combustible on, in recent years in relation to the challenges be consistent with the conservation measures of the earth谭境, necessary to suppress the co 9 to be discharged from the incinerator is generated, which has relied so far as "incineration" to "landfill" in the It has become necessary to fundamentally change the treatment method for municipal waste.
実際に、 新しい処理方式の一つとして、 可燃性廃棄物の燃料化技 術の開発が世界的に注目されるようになった。 廃棄物を燃料化し、 天然 (化石) 燃料に代替することを目的に、 広範な研究が各国で進 められ、 都市ごみ問題の解決はもちろん、 c o 2 の排出量の抑制、 化石燃料の使用量の削減などにより、 地球環境保全に向けての効果 が期待されるようになつた。 廃棄物の燃料化は、 すでに 1 9 7 0年 代当初から多く試みられ、 特に石油危機を契機に U S Aなどでは大 型プロジェク トが実施しされている。 しかしながら、 これらの試み の殆どが次のような理由で成果を上げるに到っていない。 Indeed, as one of the new treatment methods, the development of technology for converting combustible waste into fuel has gained worldwide attention. The waste fuel of natural (fossil) for the purpose of alternative fuel, extensive research is advanced in each country Merare, of course solve urban waste problems, the suppression of emissions of co 2, the amount of fossil fuel With the reduction of emissions, the effects on global environmental conservation have come to be expected. Many attempts have been made to convert waste into fuel since the early 1970s, and large-scale projects have been implemented in the United States and elsewhere, especially in the wake of the oil crisis. However, most of these attempts have not been successful for the following reasons.
第一の理由は、 廃棄物の中に含まれているガラス屑や鉄屑などが 燃料製造ブラン トの安定運転を妨げてきた。 更に、 製品自体がごみ 質の変化に伴って、 時間的に、 地域的に変化し、 安定した品質を確 保することが困難であった。 選別などの前処理を設けているが、 こ の場合でもコス ト高ゃ工場の作業環境が悪いなどの問題が技術の普 及を妨げてきた。  The first reason is that glass scraps and iron scraps contained in wastes have hindered the stable operation of fuel manufacturing brands. Furthermore, the quality of the products themselves has changed over time and regions with changes in the quality of waste, making it difficult to ensure stable quality. Pretreatment such as sorting is provided, but even in this case, problems such as the bad working environment of the high-cost factory hindered the spread of technology.
第二の理由は、 可燃性廃棄物の中に含まれている有機物が生物学 的に不安定であり、 燃料として用いられる場合に悪臭の発生、 メ タ ンガスの発生、 生成物の崩壌などの原因となり、 工場内外の環境に 悪い影響を与え、 輪送や貯蔵の操作過程でも トラブルを生じた。 そ ればかりではなく、 メ タンガスが原因で火災 ·爆発事故を惹起した り した。  The second reason is that the organic matter contained in combustible waste is biologically unstable, and when used as fuel, emits offensive odors, generates methane gas, breaks down products, etc. This had a negative effect on the environment inside and outside the factory, and caused trouble in the transport and storage operations. In addition, methane gas caused fire and explosion accidents.
第三の理由は、 化石燃料の市場価格が安値安定化する傾向の中で 燃料化した場合でもこれを受け入れていく発電所のボイラー、 セメ ン トキルンなどの技術開発が遅延し、 燃料の安定した市場を確保す ることを妨げていた。 特に、 従来の燃料化技術では、 3 5 0 0カロ ― ^ ― The third reason is that, despite fossil fuel market prices tending to stabilize at low prices, technological development of boilers and cement kilns at power plants that accept fuels has been delayed, resulting in a stable fuel supply. It was preventing the market from being secured. In particular, with conventional fuel technology, 350 calories -^-
リー前後のものが多く 、 単独で燃料として用いる場合には、 ボイラ —などの効率を下げるというマイナスもあった。 In many cases, the fuel is used alone, and when used alone as a fuel, the boiler has a negative effect of lowering the efficiency.
この発明の第一の目的は、 これまでの 「焼却」 と 「埋立」 に頼つ てきた廃棄物処理の方法を改め、 いわゆる可燃性廃棄物を再生資源 と して活用しうる物質に転換することにあり、 特に、 その用途とし て天然燃料に代替しうる 「燃料化」 の面でこれまで直面してきた上 記の困難な理由を解決する廃棄物による固形物の製造方法を提供す し とにめ O 0 The first object of the present invention is to improve the conventional waste disposal method that relied on incineration and landfill, and to convert so-called combustible waste into substances that can be used as recycled resources In particular, the present invention provides a method for producing solids from waste, which solves the above-mentioned difficult reasons that have been faced in the field of `` fuel conversion '', in which natural fuels can be used as substitutes. Nime O 0
この発明の第二の目的は、 廃棄物中に含まれる炭水化物、 蛋白質、 脂肪などを主体とする腐敗し易い有機質をアル力リ土類金属酸化物 などの添加物によって化学的 ·物理的に処理し、 生物学的に安定し た状態の物質に変化させ、 これによつて長期保存と安定な燃焼が可 能な固形燃料を製造する方法を提供することにある。  A second object of the present invention is to chemically and physically treat perishable organic substances, mainly carbohydrates, proteins, fats, etc., contained in waste with additives such as alkaline earth metal oxides. Another object of the present invention is to provide a method for producing a solid fuel that can be converted into a biologically stable substance, thereby enabling long-term storage and stable combustion.
更に、 この発明の第三の目的は、 この結果製造可能となった 「当 該プロダクツ」 を単独または石炭との混焼する方法、 他の天然燃料 との混合によるハイプリ ッ ド燃料を製造する方法を提供することに ある。  Furthermore, a third object of the present invention is to provide a method for producing the hybrid fuel by mixing the resulting "products" alone or in combination with coal, and mixing with other natural fuels. It is to provide.
加えて、 この発明の第四の目的は、 既存の焼却技術を環境保全の 面から改善するために、 廃棄物の前処理工程を設けて当該発明によ る化学反応と物理操作を施し、 これを改質することによって、 廃棄 物の貯留過程における工場の環境衛生、 悪臭発生の防止の効果をも たらすとともに、 燃焼過程においては添加した C a 0 2 などのアル 力 リ土類金属の作用で排ガスをク リーンにする効果をもたらす固形 物の焼却方法を提供することにある。 In addition, a fourth object of the present invention is to provide a waste pre-treatment step to carry out the chemical reaction and physical operation according to the present invention in order to improve the existing incineration technology from the aspect of environmental protection. the by modifying, plant sanitation in storage process of the waste, with dripping also the effect of prevention of odor-causing, at C a 0 2 effects of Al force Li earth metals, such as added in the combustion process It is an object of the present invention to provide a method for incinerating solids that has the effect of cleaning exhaust gas.
発明の開示  Disclosure of the invention
この発明は、 都巿ごみなどの廃棄物を廃棄物受入れ槽に投入した 後、 第 1破砕機, 第 2破砕機, 混合聍留反応器を経て乾燥中和反応 器で乾燥固化して固形物を製造する際に、 アル力リ土類金属酸化物 の前記廃棄物の特性に応じた添加量を添加して合理的に物理 · 化学 反応処理を行なう ことを特徵とする、 庳棄物による固形物の製造方 法である。 . According to the present invention, after the waste such as municipal waste is put into a waste receiving tank, it is solidified by a dry neutralization reactor through a first crusher, a second crusher, and a mixed distillation reactor. When manufacturing, the addition amount of the alkaline earth metal oxide according to the characteristics of the waste is added to rationalize physical and chemical This is a method for producing solids from waste, which is characterized by conducting a reaction treatment. .
前記廃棄物による固形物の製造方法において、 前記廃棄物受入れ 槽または第 1破砕機で前記廃棄物に対してアル力 リ土類金属酸化物 の全添加量の 0 〜 3 0 %を添加して物理 ·化学反応処理すること、 または前記第 2破砕機において、 前記廃棄物に対してアル力リ土類 金属酸化物の全添加量の 0〜 5 0 %を添加して物理 · 化学反応処理 すること、 あるいは、 前記混合貯留反応器において、 前記廃棄物に 対してアル力リ土類金属酸化物の全添加量の 2ひ〜 1 0 0 %を添加 して物理 · 化学反応処理を行なう こと、 さらには、 前記廃棄物受入 れ槽、 第 1破砕機、 第 2破碎機および混合貯留反応器の複数箇所に おいてアル力 リ土類金属酸化物の全添加量を適宜な比率で添加して 物理 ·化学反応処理することが望ま しい。  In the method for producing a solid material from the waste, the waste receiving tank or the first crusher is added with 0 to 30% of the total amount of the alkaline earth metal oxide added to the waste. Physical and chemical reaction treatment, or in the second crusher, physical and chemical reaction treatment by adding 0 to 50% of the total addition amount of alkaline earth metal oxide to the waste. Alternatively, in the mixed storage reactor, a physical and chemical reaction treatment is performed by adding 2 to 100% of the total amount of the alkaline earth metal oxide to the waste. Further, the total amount of the alkaline earth metal oxide is added at an appropriate ratio in a plurality of locations of the waste receiving tank, the first crusher, the second crusher, and the mixed storage reactor. It is desirable to perform physical and chemical reaction treatment.
また、 この発明は、 廃棄物にアルカリ土類金属酸化物を添加して 固形物を製造するに際して、 水分 W %、 プラスチック P %、 無機物 M %および資源化物 R %を分析測定して、 U = 1 0 0— ( W + P + M + R ) に基づき有機物 U %を算出すると共に、 アルカリ土類金属 酸化物の最適な添加量 Aを、 A = K X U [但し、 K = f ( P , W ) ] を基にし決定して廃棄物にアル力リ土類金属酸化物を添加すること を特徵とする廃棄物による固形物の製造方法である。 前記 Kの値が 0 . 2〜 1 . 2の範囲であることが好ましい。  In addition, the present invention provides a method for manufacturing a solid by adding an alkaline earth metal oxide to waste, analyzing and measuring water W%, plastic P%, inorganic M%, and resource R%, U = 1 0 0— (W + P + M + R), calculate the organic matter U%, and determine the optimal addition amount A of the alkaline earth metal oxide as A = KXU [where K = f (P, W )] And a method for producing solids from wastes, characterized by adding an alkaline earth metal oxide to the wastes. Preferably, the value of K is in the range of 0.2 to 1.2.
上記の発明によれば、 都市ごみなどの廃棄物から廃棄物受入れ槽, 第 1破砕機, 第 2破砕機, 混合貯留反応器および乾燥中和反応器を 経て、 前記廃棄物受入れ槽, 第 1破砕機, 第 2破碎機, および混合 貯留反応器のいずれか或いは複数箇所の工程に適宜なアル力リ土類 金属酸化物を添加して物理 · 化学反応処理することによって、 とく に、 ク リーンな燃料や土木建築材料の素材に有効な固形物を得るこ とができる。  According to the above invention, the waste receiving tank, the first crusher, the second crusher, the mixed storage reactor, and the dry neutralization reactor pass through the waste receiving tank, the first crusher, the second crusher, and the like from the municipal waste. By adding an appropriate alkaline earth metal oxide to one or more of the crusher, the second crusher, and the mixed storage reactor, and performing a physical and chemical reaction treatment, It is possible to obtain solids that are effective as fuels and materials for civil engineering and construction materials.
また、 このようにして得られた固形物は、 物理的、 化学的、 生物 1 The solids obtained in this way are physically, chemically and biologically 1
5 学的に安定化されているので、 長期貯蔵することができると共に、 ガス爆発や粉じん爆発が発生しない固形物であり、 ク リーンな燃料 . や土木建築材料の素材と して有効に利用されるものである。  5 Since it is chemically stabilized, it can be stored for a long period of time and is a solid that does not cause gas explosion or dust explosion.It is effectively used as a material for clean fuel and civil engineering and building materials. Things.
また、 上記各工程において添加するアル力 リ土類金属酸化物は、 都市ごみなどの廃棄物を構成する水分, プラスチッ ク, 無機物, 資 源化物を分析、 測定することにより、 有機物 11の%を算出し、 この 有機物 Uの%を基にして有効かつ最適な添加量を得ることができる。  The alkaline earth metal oxide added in each of the above processes can reduce 11% of organic matter by analyzing and measuring water, plastics, inorganic substances, and resource substances that constitute waste such as municipal solid waste. It is possible to calculate and obtain an effective and optimum addition amount based on the percentage of the organic matter U.
また、 この発明は、 予め破砕され不燃物を除去された廃棄物を適 宜な量のアル力 リ土類金属酸化物を含んだ添加材を混台貯留反応器 に投入して混合 · 反応を行なった後、 反応された第 1生成廃棄物を 混合脱気反応器に投入し、 適宜な量のアルカ リ土類金属酸化物を含 んだ添加材を必要に応じて添加し、 混合反応および反応生成ガスの 脱気を行ない、 反応された第 2生成廃棄物を圧縮成型機に投入して 圧縮成型を行ない、 次いで、 圧縮成型された第 3生成廃棄物を乾燥 中和反応器に投入して乾燥中和反応を行ない、 さらに必要に応じて 篩分器にて篩分して固形物燃料を得る廃棄物による固形物燃料の製 造 'ある。  In addition, the present invention provides a mixing and storage reactor in which an appropriate amount of an additive containing alkaline earth metal oxide is charged into a mixing and storage reactor, and the waste which has been previously crushed and from which incombustibles have been removed is added. After the reaction, the reacted first product waste is charged into a mixed degassing reactor, and an appropriate amount of an additive containing an alkaline earth metal oxide is added as necessary, to perform the mixing reaction and The reaction product gas is degassed, the reacted second product waste is put into a compression molding machine to perform compression molding, and then the compression molded third product waste is put into a dry neutralization reactor. Dry neutralization reaction, and, if necessary, sieving with a sieving machine to obtain solid fuel.
また、 前記製造方法において、 前記混合貯留反応器における反応 を密閉状態下、 温度 6 0 以上 1 0 0て以下で 1時間以上行ない、 混合脱気反応器における反応を排気状態下、 前記温度より少く とも 5 以上高い温度で 5分間以上行なうのが好ま しい。  Further, in the production method, the reaction in the mixed storage reactor is performed in a closed state, at a temperature of 60 to 100 and at a temperature of not more than 1 hour, and the reaction in the mixed deaeration reactor is performed in an exhausted state. It is preferable to perform at least 5 minutes at a higher temperature for at least 5 minutes.
さらに、 前記廃棄物による固形物燃料の製造方法において、 予め 細破砕された廃棄物とするために、 廃棄物を第 1破砕機で粗破砕す ると共に不燃物を選別除去し、 次いで破砕された廃棄物に適宜な量 のアル力リ土類金属酸化物を含んだ添加剤を投入し、 第 2破砕機で 破砕すると共に廃棄物の複合材中に含まれている不燃物を選別除去 し、 さらに、 第 3破砕機で細破砕された廃棄物とすること、 さらに、 前記反応された第 1生成廃棄物、 前記脱気反応された第 2生成廃棄 物、 あるいは前記篩分器にて篩分された粉体の廃棄物を必要に応じ てかつ、 必要な量だけ前記混合貯留反応器に還流することが望ま し い。 Further, in the method for producing a solid fuel from the waste, the waste was coarsely crushed by a first crusher and non-combustibles were selectively removed in order to obtain finely crushed waste, and then crushed. An appropriate amount of additive containing alkaline earth metal oxide is added to the waste, crushed by the second crusher, and the incombustibles contained in the composite material of the waste are separated and removed. Further, the waste is finely crushed by a third crusher, and further, the reacted first generated waste, the degassed second generated waste, or sieved by the sieve. Powder waste as needed At the same time, it is desirable to reflux only a necessary amount to the mixed storage reactor.
上記の発明によれば、 ごみなどの廃棄物からク リーンな燃料とな る固形物を得ることができる。 また、 この得られた固形物は、 物理 的、 化学的、 生物学的に安定化されているので、 長期貯蔵すること ができる。 さらに、 ガス爆発や粉じん爆発が発生しない、 安全な廃 棄物燃料を提供することができる。  According to the above-mentioned invention, a solid material serving as a clean fuel can be obtained from waste such as refuse. The resulting solids are physically, chemically and biologically stabilized and can be stored for long periods of time. In addition, it is possible to provide safe waste fuel without gas or dust explosion.
しかも、 各工程で充分な特性が得られていない場合には還流させ ているから、 品質の安定した固形物燃料を得ることができる。  In addition, when sufficient characteristics are not obtained in each step, reflux is performed, so that a solid fuel with stable quality can be obtained.
また、 この発明は、 廃棄物による固形物燃料に、 天然燃料を混合 した後、 圧縮成型加工あるいは造粒加工を行なう ことを特徵とする ハイプリ ッ ド燧料の製造方法である。  Further, the present invention is a method for producing a hybrid flint, which comprises performing a compression molding process or a granulation process after mixing a natural fuel with a waste solid fuel and then subjecting the mixed fuel to a natural fuel.
この発明によれば、 ハイブリ ツ ド燃料には、 廃棄物燃料が一定の 割台で含有されているため従来の 1 0 0 %の天然燃料のコス トに比 ベて安価に製造することができる。 また、 固形物燃料には C a 0な どのアル力リ土類金属酸化物が含まれていることにより、 排ガスに 含まれる酸性ガスの吸収が行なわれて、 環境汚染のないク リーンな 燃料とすることができる。  According to the present invention, the hybrid fuel contains waste fuel at a constant rate, and therefore can be manufactured at a lower cost than the conventional cost of 100% natural fuel. . In addition, since solid fuel contains alkaline earth metal oxides such as Ca0, it absorbs acidic gas contained in exhaust gas, resulting in a clean fuel with no environmental pollution. can do.
. このハイブリ ツ ド燃料は、 例えば簡易型ス トーブなどの小型ボイ ラー用の燃料として使用可能であると共に、 品位としては無煙炭に 近く なり、 さらに廃棄物による固形物燃料を含有しているから繊維 質が、 バイ ンダ一としての効果があり、 造粒しやすく なる。 発熱量 としては天然燃料と廃棄物による固形物燃料の中間の低品位石炭並 のカロリーを有し、 産業用燃料として充分使用可能であり、 種々な 燃料の多く の用途に使用できるものである。  This hybrid fuel can be used as fuel for small boilers such as simple stoves, etc., and its quality is close to that of anthracite, and it contains solid fuel from waste. The quality is as effective as a binder, making it easier to granulate. It has a calorific value equivalent to that of low-grade coal, which is intermediate between solid fuels made from natural fuels and wastes, and can be sufficiently used as industrial fuels, and can be used for many uses of various fuels.
さらに、 この発明は、 都市ごみなどの廃棄物を廃棄物受入れ槽に 投入した後に焼却炉に投入して廃棄物を焼却する際、 前記廃棄物受 入れ槽にアルカ リ土類金属酸化物の前記廃棄物の特性に応じた添加 量を添加して合理的に物理 · 化学反応処理を行なう ことを特徵とす る廃棄物の焼却方法である。 Further, the present invention provides a method for manufacturing a waste container, comprising: inserting waste such as municipal solid waste into a waste receiving tank, and then charging the waste into an incinerator to incinerate the waste; It is characterized in that the physical and chemical reaction treatment is performed rationally by adding the amount according to the characteristics of the waste. Waste incineration method.
また、 都市ごみなどの廃棄物を廃棄物受入れ槽に投入した後、 第 1破砕機を経て焼却炉に投入して廃棄物を焼却する際、 前記廃棄物 受入れ槽および第 1破砕機の両方またはいずれか一方にアルカ リ土 類金属酸化物の前記廃棄物の特性に応じた添加量を添加して合理的 に物理 · 化学反応処理を行なう ことを特徴とする廃棄物の焼却方法 し'ある。  When waste such as municipal solid waste is put into the waste receiving tank, and then put into the incinerator via the first crusher to incinerate the waste, both the waste receiving tank and the first crusher or A waste incineration method characterized by adding an amount of an alkaline earth metal oxide according to the properties of the waste to one of the two and rationally performing a physical / chemical reaction treatment.
都市ごみなどの廃棄物を廃棄物受入れ槽に投入した後、 第 1破砕 機, 第 1選別機および第 2破砕機を経て焼却炉に投入して廃棄物を 焼却する際、 前記廃棄物の特性に応じて前記廃棄物受入れ槽, 第 1 破砕機および第 2破砕機のいずれかまたは複数箇所にアル力 リ土類 金属酸化物の適宜な量を添加して合理的に物理, 化学反応処理を行 なう ことを特徴とする廃棄物の焼却方法である。  When waste such as municipal solid waste is put into a waste receiving tank and then put into an incinerator via a first crusher, a first sorter and a second crusher to incinerate the waste, the characteristics of the waste The appropriate amount of alkaline earth metal oxide is added to one or more of the waste receiving tank, the first crusher and the second crusher according to This is a waste incineration method characterized by the following:
都市ごみなどの廃棄物を廃棄物受入れ槽に投入した後、 第 1破砕 機, 第 1選別機, 第 2破砕機, 第 2選別機および混合聍留反応器を 経て焼却炉に投入して廃棄物を焼却する際、 前記廃棄物の特性に応 じて、 前記廃棄物受入れ槽, 第 1破砕機, 第 2破砕機および混合貯 留反応器のいずれかまたは複数箇所にアル力 リ土類金属酸化物の適 宜な量を添加して合理的に物理 · 化学反応処理を行なう ことを特徴 とする廃棄物の焼却方法である。  After the waste such as municipal waste is put into the waste receiving tank, it is put into the incinerator via the first crusher, the first sorter, the second crusher, the second sorter, and the mixed distillation reactor, and is disposed of. At the time of incineration of the waste, according to the characteristics of the waste, one or more of the waste receiving tank, the first crusher, the second crusher, and the mixed storage reactor may be used as alkaline earth metal. This is a waste incineration method characterized in that an appropriate amount of oxide is added and a physicochemical reaction is performed rationally.
上記の発明によれば、 廃棄物受入れ槽, 第 1破砕機, 第 2破砕機 または混合貯留反応器までの処理工程でアル力リ土類金属酸化物を 適宜な量だけ添加して物理 · 化学反応処理を行なつて焼却炉に投入 して焼却処理を行なう ことにより、 化水による腐食を防止でき、 か つ塩化水素や硫黄酸化物などの酸性ガスを除外することができ、 高 効率でク リ ーンなエネルギーを得ることができる。 また石炭火カブ ラ ン トにおいてごみとの混焼を行なう場合にも効率的に適用可能で め  According to the invention described above, an appropriate amount of alkaline earth metal oxide is added in the processing steps up to the waste receiving tank, the first crusher, the second crusher, or the mixed storage reactor to provide physical and chemical By injecting into the incinerator after performing the reaction treatment, the incineration treatment can prevent corrosion due to water formation, eliminate acidic gases such as hydrogen chloride and sulfur oxides, and achieve high efficiency You can get lean energy. It can also be applied efficiently to co-firing with refuse in coal-fired plants.
図面の簡単な説明 第 1図はこの発明を実施する一実施例の収集された廃棄物から固 形物 (燃料) を得ると共に、 中間生成物を焼却する概念的な工程図 を示すものである。 BRIEF DESCRIPTION OF THE FIGURES FIG. 1 shows a conceptual process diagram for obtaining solids (fuel) from collected waste and incinerating an intermediate product according to an embodiment of the present invention.
第 2図は、 第 1図に示された工程で得られた廃棄物による固形物 燃料と天然燃料を混合してハイブリ ッ ド燃料を製造する製造方法の 一実施例の工程図を示すものである。  FIG. 2 shows a process chart of an embodiment of a production method for producing a hybrid fuel by mixing solid fuel and natural fuel by the waste obtained in the process shown in FIG. is there.
発明を実施するための最良の形態  BEST MODE FOR CARRYING OUT THE INVENTION
この発明をより詳細に説明するために、 添付の図面に従ってこれ を説明する。  The present invention will be described in more detail with reference to the accompanying drawings.
第 1図はこの発明を実施する一実施例の収集された廃棄物から固 形物を得ると共に、 中間生成物を焼却する概念的な工程図を示すも のである。  FIG. 1 is a conceptual diagram showing a process for obtaining solids from collected waste and incinerating an intermediate product according to an embodiment of the present invention.
第 1図を参照するに、 例えば一般家庭あるいは事業所から排除さ れるごみなどの廃棄物 Gは、 紙, ダンボール, 纖維類などの可燃物 と、 鉄, アルミ, ガラス, 土などの不燃物と、 これに含まれる水分 などで構成されており、 トラッ ク, パッカー車などの運搬車などで 運ばれてきて、 一旦ピッ トなどからなる廃棄物受入れ槽 1に投入さ れる。 この廃棄物受入れ槽 1から必要な量だけ、 必要な時期に第 1 破砕機 3に投入される。  Referring to Fig. 1, for example, waste G such as garbage removed from households and offices is composed of combustible materials such as paper, cardboard and fiber, and non-combustible materials such as iron, aluminum, glass, and soil. It is composed of the water contained therein, is transported by trucks, packers, and other transport vehicles, and is once put into a waste receiving tank 1 consisting of pits and the like. From the waste receiving tank 1, only the required amount is fed into the first crusher 3 at the required time.
第 1破砕機 3は例えば油圧低速駆動型の引裂き破砕機で、 具体的 な構造は公知であるため、 詳細な説明は省略するが、 回転数がそれ ぞれ異なる 2または 3軸を有し、 各軸の外周にはそれぞれ複数の刃 力《備えられている。  The first crusher 3 is, for example, a hydraulic low-speed driven tear crusher, and its detailed structure is omitted because its specific structure is publicly known, but it has two or three shafts whose rotation speeds are different from each other, The outer periphery of each shaft is provided with a plurality of blade forces.
而して、 投入された廃棄物 Gを、 回転数がそれぞれ異なる 2また は 3軸の回転引裂刃により く わえ込み、 引裂き、 強固なものまで突 き破って、 低速、 高トルクの油圧駆動によりゆっ く り引裂かれ、 本 体下部の排出口から排出される。 なお、 この第 1破砕機 3の駆動は 油圧駆動方式となっており、 可変吐出アキシャルピス ト ンポンプを 使用することにより、 通常負荷時は、 高速, 低トルクにて、 負荷増 大時に低速, 高トルク運転と負荷の必要に応じて軸回転数を可変と することができるため、 破砕負荷については、 常時最適状態にて運 転制御が可能となつている。 Thus, the input waste G is gripped by a two- or three-axis rotary tearing blade with different rotational speeds, tears through, breaks through to a strong one, and is driven by a low-speed, high-torque hydraulic drive. Is slowly torn and discharged from the outlet at the bottom of the body. The drive of the first crusher 3 is of a hydraulic drive type. By using a variable discharge axial piston pump, the load can be increased at high speed and low torque under normal load. Since the shaft speed can be varied according to the need for low-speed, high-torque operation and load during large hours, operation control can always be performed in an optimal state for the crushing load.
この第 1破砕機 3で粗破砕された第 1廃棄物 G 1 は、 例えばベル トコンベアなどからなる第 1選別機 5に送られる。 この第 1選別機 5には磁選機が備えられていて、 この磁選機により鉄, 非鉄などの 金属が除去されると共に有害危険物などが除去される。 また、 第 1 選別機 5では、 ビン, ブロッ クなどの中粒無機物が選別されて除去 される。  The first waste G 1 roughly crushed by the first crusher 3 is sent to a first sorter 5 composed of, for example, a belt conveyor. The first separator 5 is provided with a magnetic separator, which removes metals such as iron and non-ferrous metals and harmful hazardous materials. In the first sorter 5, medium-sized inorganic substances such as bottles and blocks are sorted and removed.
第 1選別機 5で金属, 無機物が除去されると、 第 2廃棄物 G 2は 第 2破砕機 7に送られる。 第 2破砕機 7は例えばハンマ ミ ルなどか らなっており、 この第 2破砕機 7で廃棄物 G 2はさらに細かく破砕 される。  When metals and inorganic substances are removed by the first sorter 5, the second waste G 2 is sent to the second crusher 7. The second crusher 7 is made of, for example, a hammer mill. The second crusher 7 further crushes the waste G2.
この第 2破砕機 7で細かく破砕された第 3廃棄物 G 3は、 例えば 選別機, 篩分器, 比重差分離機などからなる第 2選別機 9に送られ る。 この第 2選別機 9では、 第 1選別機 5で除去しきれなかった钿 かな金属や無機物が除去されて、 第 4廃棄物 G 4が第 3破砕機 1 1 に送られる。 第 3破砕機 1 1は例えばリ ンググライダー ミ ルなどを 用い、 第 4廃棄物 G 4を更に钿破砕する。 た し、 第 2破砕機 7で 必要な破砕粒度が得られる場合には第 3破砕機 1 1 に投入せずに省 略してもよい。  The third waste G3 finely crushed by the second crusher 7 is sent to a second separator 9 including, for example, a separator, a sieve, a specific gravity separator, and the like. In the second sorter 9, metal and inorganic substances that could not be completely removed by the first sorter 5 are removed, and the fourth waste G 4 is sent to the third crusher 11. The third crusher 11 further crushes the fourth waste G4 by using, for example, a ring glider mill. However, when the required crush particle size can be obtained in the second crusher 7, the crusher may be omitted without being charged into the third crusher 11.
第 2破砕機 7に第 1選別機 5で選別された第 2廃棄物 G 2と共に 適宜な量の C a 0などのアル力リ土類金属酸化物を含んだ添加材が 投入される。 このため第 2廃棄物 G 2は破砕されると共に、 アル力 リ土類金属酸化物である C a Oと均一に混合し接触される。 接触さ れると、 アルカ リ土類金属酸化物である C a 0が第 2廃棄物 G 2に 含まれている水分 (H 2 0 ) とが反応して C a ( O H ) 2 となり、 この C a ( O H ) 2 が固体である第 2廃棄物 G 2中に分散される。 この反応は第 2破砕機 7内ではじまり、 次の第 2選別機 9 , 第 3破 砕機 1 1を経て混合貯留反応器 1 3内で完了する。 このアルカ リ土 類金属酸化物である C a 0の投入量は廃棄物の投入量に対して 2 〜 5 %、 好ましく は 3 %程度を投入する。 Into the second crusher 7, an appropriate amount of an additive containing an alkaline earth metal oxide such as Ca 0 is fed together with the second waste G 2 sorted by the first sorter 5. As a result, the second waste G 2 is crushed and uniformly mixed and contacted with the alkaline earth metal oxide C a O. Once contacted, C a (OH) 2 becomes the C a 0 is alkali earth metal oxide and water (H 2 0) included in the second waste G 2 are reacted, the C a (OH) 2 is dispersed in the solid second waste G2. This reaction starts in the second crusher 7, and the next second sorter 9 and third crusher It is completed in the mixed storage reactor 13 through the crusher 11. The input amount of the alkaline earth metal oxide Ca 0 is 2 to 5%, preferably about 3%, based on the input amount of the waste.
第 3破砕機 1 1で細破砕された第 5廃棄物 G 5と適宜な量のアル 力リ土類金属酸化物である C a 0が混合貯留反応器 1 3に投入され る。 混合貯留反応器 1 3は例えば回転式 6角ミキサ, リボンミ キサ, あるいは移動スク リ ユー式攪拌機などからなっていて、 貯留されな がら一定時間混合される。 この混合貯留反応器 1 3を必要に応じて、 熱風や加熱チュ一ブでもつて加熱せしめることにより、 反応速度を 早く させることができる。 密閉状態下、 例えば温度 6 0 以上 1 〇 〇 以下で 1時間以上行なうのが好ま しい。  Fifth waste G5 finely crushed by the third crusher 11 and an appropriate amount of alkaline earth metal oxide Ca0 are charged into the mixed storage reactor 13. The mixed storage reactor 13 is composed of, for example, a rotary hexagonal mixer, a ribbon mixer, or a moving screw-type stirrer, and is mixed for a certain period of time while being stored. The reaction rate can be increased by heating the mixed storage reactor 13 with hot air or a heating tube if necessary. It is preferable to conduct the treatment in a closed state, for example, at a temperature of 60 to 1 1 〇 for 1 hour or more.
この混合貯留反応器 1 3で反応して生成された第 6廃棄物 G 6 (第 1生成廃棄物) と必要に応じて適宜な量のアルカリ土類金属酸 化物である C a 0を含んだ添加材が混合脱気反応器 1 5に投入され て、 混合反応されると共に、 アンモニアなどを脱気する。 すなわち、 排気状態下、 前記温度より少なく とも 5 以上高い温度で 5分間以 上行なうのが好ま しい。 次いで、 反応された第 7廃棄物 G 7 (第 2 生成廃棄物) を圧縮成型機 1 7に投入して、 圧縮作用によって密度 を高めた上で、 押出して粒状に成型される。 この圧縮成型機 1 7で 粒状に成型された第 8廃棄物 G 8 (第 3生成廃棄物) は乾燥中和反 応器 1 9に投入される。 この乾燥中和反応器 1 9では、 温度を 1 3 0 〜 2 3 0 まで上げ、 殺菌を行ない、 熱化学変化を完了させると 共に、 水分を除く と同時に、 添加材のアルカリ (C a C o H ) 2 な どを c o 2 ガスで中和し固化させることによつて固形物 Sが得られ る。 The mixed storage reactor 13 contained the sixth waste G 6 (first generated waste) generated by the reaction and an appropriate amount of alkaline earth metal oxide C a 0 as necessary. The additive material is introduced into the mixed degassing reactor 15 to perform a mixing reaction and degas ammonia and the like. That is, it is preferable to perform the heating at a temperature at least 5 or more higher than the above-mentioned temperature for 5 minutes or more under the exhaust state. Next, the reacted seventh waste G7 (second waste product) is put into a compression molding machine 17, where the density is increased by a compression action, and then extruded to be formed into granules. The eighth waste G 8 (third generated waste) formed into granules by the compression molding machine 17 is supplied to the dry neutralization reactor 19. In this dry neutralization reactor 19, the temperature is raised to 130 to 230, sterilization is performed, thermochemical changes are completed, moisture is removed, and at the same time, the alkali (Ca Co) H) 2 etc. are neutralized with co 2 gas and solidified to obtain a solid S.
こ う して得られた固形物 Sは、 必要に応じて篩分器 2 1で篩分き れて固形物燃料と して取り出きれたり、 あるいは土木建築資材用素 材として取り出されて使用されて産業界に広く適用されるものであ o すなわち、 混合貯留反応器 1 3から乾燥中和反応器 1 9までの間 で次のような作用が生じる。 The solid matter S thus obtained can be sieved with a sieve 21 as needed to be taken out as a solid fuel, or taken out as a material for civil engineering and building materials and used. Is widely applied to industry That is, the following operation occurs between the mixed storage reactor 13 and the dry neutralization reactor 19.
有機質中に含まれる蛋白質, 糖質, 脂質は熱とアルカ リの作用に よって変性し、 一部は加水分解される。 アルカ リの作用と機械的作 用により、 紙, 木材, 植物残渣などが、 繊維状にほぐれると共に細 菌は死滅する。  Proteins, carbohydrates, and lipids contained in organic matter are denatured by the action of heat and alkali, and some are hydrolyzed. By the action of alkali and mechanical action, paper, wood, plant residues, etc. are loosened in a fibrous form and bacteria are killed.
また、 有機質の腐敗または分解によって生じた酸性物質 (H n S , 有機酸など) は中和され、 アンモニアは揮発すると共に、 水分が蒸 発し、 残物は乾燥される。  In addition, acidic substances (HnS, organic acids, etc.) generated by organic spoilage or decomposition are neutralized, ammonia evaporates, moisture evaporates, and the residue is dried.
未反応 C a ( O H ) 2 は乾燥中和反応器 1 9内で乾燥用ガス中の C 0 0 で中和され、 不溶性の C a C O。 が生ずる。 Unreacted C a (OH) 2 is neutralized with C 00 in the drying gas in a drying neutralization reactor 19 to form insoluble C a CO. Occurs.
最終的には、 添加材は脱水と C a C 0 3 生成で固結し、 他の物質 を結びつけ、 微粒化された廃棄物は低水分と C a ( O H ) „ のアル 力 リ性により生物学的に安定化される。 Biological Finally, additional material is consolidated in the dried and C a C 0 3 generates, combines the other substances, atomized waste by Al force Li of low moisture and C a (OH) " Is chemically stabilized.
このようにして得られた粒状の廃棄物は、 必要に応じて篩分器 2 1で篩分されて固形物としての固形物燃料 Sが取り出されるのであ る c  The granular waste thus obtained is sieved by a sieving device 21 as necessary to remove solid fuel S as a solid.c
この篩分器 2 1で篩分された固形物のうち、 一定の大きさより小 さな粉体は、 一定の大きさを满足していないため、 必要に応じて混 合聍留反応器 1 3に還流されて再度投入される。  Of the solids sieved by the sieving device 21, powder smaller than a certain size does not have a certain size. Refluxed and recharged.
前記混合貯留反応器 1 3で貯留されながら混合された第 6廃棄物 G 6は、 混合脱気反応器 1 5に投入される前に、 品質の安定化がチ エ ッ クされて、 一定の品質に達成していなければ、 混合貯留反応器 1 3に還流される。 この還流される比率は、 混合聍留反応器 1 3に おける反応時間, 反応条件により異なるが、 最大 5 0 %還流させれ ば十分である。 要は第 6廃棄物 G 6の品質が一定の品質を满足する と、 混合脱気反応器 1 5に投入される。  The sixth waste G6 mixed while being stored in the mixed storage reactor 13 is checked for quality stabilization before being fed into the mixed degassing reactor 15, and a certain If the quality has not been achieved, it is returned to the mixed storage reactor 13. The ratio of this reflux depends on the reaction time and reaction conditions in the mixed distillation reactor 13, but it is sufficient to reflux up to 50%. In short, when the quality of the sixth waste G6 satisfies a certain level, it is fed into the mixed degassing reactor 15.
また、 混合脱気反応器 1 5で反応された第 7廃棄物 G 7は、 圧縮 成型機 1 7に投入される前に、 一定の反応達成率が維持されている がどうかのチヱックが行なわれて、 一定の反応達成率が達成されて いなければ、 混合貯留反応器 1 3に還流される。 したがって、 一定 の反応達成率を維持した第 8廃棄物 G 8だけが圧縮成型機 1 7に投 入されるのである。 In addition, the 7th waste G7 reacted in the mixed degassing reactor 15 maintains a certain rate of reaction achievement before it is injected into the compression molding machine 17. If a certain reaction achievement rate has not been achieved after a check has been made, the mixture is returned to the mixed storage reactor 13. Therefore, only the eighth waste G8, which maintains a certain reaction achievement rate, is injected into the compression molding machine 17.
このように、 混合貯留反応器 1 3で反応された第 6廃棄物 G 6, 混合脱気反応 1 5で反応された第 7廃棄物 G 7あるいは乾燥中和反 応器 1 9で乾燥 · 中和されて篩分器 2 1で篩分された固形物が、 一 定の物質的組成、 一定の反応達成率および一定の大きさになるまで 何回でもフィ 一 ドバックされるようにしてあるから、 最終的に得ら れる固形物 (燃料) は均質でク リーンな燃料として取り出すことが できる。  Thus, the sixth waste G 6 reacted in the mixed storage reactor 13, the seventh waste G 7 reacted in the mixed degassing reaction 15 or dried and neutralized in the dry neutralization reactor 19 The solids that have been combined and sieved in the sieve 21 are fed back many times until they reach a certain material composition, a certain reaction completion rate, and a certain size. However, the final solid (fuel) can be taken out as a homogeneous and clean fuel.
第 2破砕機 7から混合脱気反応器 1 5までの工程で、 アルカ リ土 類金属酸化物である C a 0を含んだ添加材を、 その各段階で必要な 量だけ投入し、 化学反応させて、 腐敗性、 悪臭を取り除く と共に、 生物学的に安定化してあるから、 得られた固形物を燃料として長期 貯蔵することができると共に、 メ タンガスが発生してガス爆発など が起きることなく、 安全な燃料として使用することができる。  In the process from the second crusher 7 to the mixed degassing reactor 15, an additive containing Ca 0, which is an alkaline earth metal oxide, is charged in the required amount in each stage, and the chemical reaction In addition to removing spoilage and odor, and biologically stabilized, the obtained solid can be stored as fuel for a long period of time, and methane gas is not generated and gas explosion does not occur. , Can be used as a safe fuel.
前記圧縮成型機 1 7で加熱圧縮成型された中間生成物である第 8 廃棄物 G 8の性状は、 燃料製造の場合と土木建築資材用素材製造の 場合と異なる。 これは圧縮成型器 1 7の機械的な性能または部品の 交換等によつて選択することは容易である。 燃料を目的とする場台 でも石炭との混焼など流動床式ボイラーに投入する場合とス トー力 一型ボイラーに投入する場合と、 その性状を選択することが必要と なる。 本実施例では、 とく に流動床式ボイラーに適した燃料として 製造する;とが機械的に負荷が少なく燃焼特性から見ても効果的で あることを確認している。 概ね 5 mm〜 l 0 mmの粒状に製造すること が機械的に容易であり、 かつ効果的である。  The properties of the eighth waste G8, which is an intermediate product heated and compression-molded by the compression molding machine 17, are different from those in the case of fuel production and in the case of civil engineering building material production. This can be easily selected based on the mechanical performance of the compression molding machine 17 or the replacement of parts. It is necessary to select the properties of fuel tanks for fuel tanks, such as co-firing with coal and charging into a fluidized-bed boiler and storage-force type boilers. In this example, it was confirmed that the production of a fuel particularly suitable for a fluidized-bed boiler is effective because of its low mechanical load and combustion characteristics. It is mechanically easy and effective to produce granules of approximately 5 mm to 10 mm.
上述した廃棄物 Gを廃棄物受入れ槽 1へ投入してから乾燥中和反 応器 1 9までの処理工程を経て固形物 Sを製造するに際して、 廃棄 物受入れ槽 1 または第 1破砕機 3に、 アルカリ土類金属酸化物とし ての例えば C a 0を、 脱臭および腐敗驍酵の抑制等を目的として都 巿ごみなどの廃棄物 Gに対して添加して物理 · 化学反応処理が行な われる。 この場台、 C a 0の添加量は全添加量の 0〜 3 0 %程度が 好ま しい。 3 0 %を越えても余り効果を発揮するものではない。 すなわち、 実際に、 廃棄物受入れ槽 1または第 1破砕機 3に C a 0を投入することによって、 これまでのこの種の施設が共通して克 服しなければならなかった都市ごみの受入貯留施設からの悪臭の発 生等を防ぐことができる。 そしてカルシウムの作用によって腐敗♦ 驟酵、 昆虫の発生などを抑制する効果がある。 When the above-mentioned waste G is put into the waste receiving tank 1 and processed through the processing steps up to the dry neutralization reactor 19 to produce the solid S, For example, C a 0 as an alkaline earth metal oxide is added to the waste receiving tank 1 or the first crusher 3 to the waste G such as garbage for the purpose of deodorization and control of spoilage enzyme. Physical and chemical reaction processes are performed. In this case, the addition amount of Ca 0 is preferably about 0 to 30% of the total addition amount. Even if it exceeds 30%, it does not show much effect. In other words, by actually introducing C a 0 into the waste receiving tank 1 or the first crusher 3, the receiving and storing of municipal solid waste that this type of facility had to overcome in common The generation of foul odors from the facilities can be prevented. The action of calcium has the effect of suppressing spoilage and the development of insects.
また、 都市ごみの解砕を行なう第 1破砕機 3においても事前に力 ルシゥ厶が投入されることによって、 悪臭の防止、 さ らには嫌気性 醱酵物の付着によるブラン トの腐食などを防止することができる。 廃棄物受入れ槽 1への投入量は全投入量の 1 0 %〜 2 0 %の範囲で 行なう ことが望ま しい。  In addition, in the first crusher 3 that disintegrates municipal solid waste, odor is introduced in advance to prevent bad smell and prevent corrosion of the brand due to adhesion of anaerobic fermentation products. can do. It is desirable that the input amount to the waste receiving tank 1 should be within the range of 10% to 20% of the total input amount.
また、 前記第 1選別機 5で選別された第 2廃棄物 G 2を第 2破砕 機 7に投入する際に、 C a 0も一緒に投入して、 混合および第 1次 の C a 0による化学反応を行なわしめる。 この場合における C a O の添加畺は、 全添加量の 0〜 5 0 %を添加して物理 ·化学反応処理 するのが望ま しい。  In addition, when the second waste G2 sorted by the first sorter 5 is charged into the second crusher 7, C a0 is also charged together, and mixed and mixed according to the first C a0. Let the chemical reaction take place. In this case, the addition of CaO is desirably performed in a physical / chemical reaction treatment by adding 0 to 50% of the total amount.
第 2破砕機 7に投入する目的は、 第 2破砕機 7内において C a 0 とごみが均一に混合すると同時に固体と固休の接触を機械的に行な い、 C a Oによる反応を促進させることができる。 従来この種の破 砕工程から発生する都市ごみの粉じんは、 生物学的に活性なもので あり、 かつ病原菌による環境への影響が少なからず認められている。 この点で、 第 2破砕機 7内に C a Oを投入することによって反応を 促すばかりではなく 、 工場内における労働環境の改善に著しい効果 をあげることができる。  The purpose of feeding into the second crusher 7 is to promote uniform reaction between C a 0 and refuse in the second crusher 7 and at the same time mechanical contact between solids and solids to promote the reaction by C a O. Can be done. Conventionally, municipal dust generated from this type of crushing process has been biologically active, and the effects of pathogenic bacteria on the environment have been recognized to some extent. In this regard, the introduction of CaO into the second crusher 7 not only promotes the reaction but also has a remarkable effect on the improvement of the working environment in the factory.
C a 0の添加率は全投入量の 1 0 %〜 2 0 %が普通である力;'、 場 合によっては 5 0 %までを投入することが妥当である。 The addition rate of C a 0 is usually 10% to 20% of the total input force; In some cases, it is appropriate to input up to 50%.
さらに、 前記混合貯留反応器 1 3に第 3破砕機 1 1で粉砕された 第 5廃棄物 G 5を投入すると同時に C a 0を投入してもよい。 この 場合における C a 0の添加量は全添加量の 2 0 %〜 1 0 0 %が望ま しい。 この工程で C a 0を投入する目的は C a Oによる反応を完結 するためのものである。  Further, the mixed storage reactor 13 may be charged with the fifth waste G5 pulverized by the third crusher 11 at the same time as charging Ca0. In this case, the added amount of Ca 0 is desirably 20% to 100% of the total added amount. The purpose of introducing C a 0 in this step is to complete the reaction with C a O.
場合によっては、 廃棄物受入れ槽 1 , 第 1破砕機 3, 第 2破砕機 7および混合貯留反応器 1 3の複数箇所に C a 0を適宜な添加量で もって添加することも可能である。  In some cases, it is also possible to add Ca 0 to a plurality of locations of the waste receiving tank 1, the first crusher 3, the second crusher 7, and the mixed storage reactor 13 in appropriate amounts.
したがって、 C a 0を添加し、 都市ごみと反応させ、 物理 · 化学 反応処理で安定な物質に転換し、 かつアンモニアなどの N 0 X成分 をごみの中から除外するための工程である。 圧縮成型された粒状の 中間生成物は、 加熱と C a 0の発熱反応によって 5 0 以上の温度 を持っている。  Therefore, it is a process for adding Ca 0, reacting with municipal solid waste, converting it to a stable substance by physical and chemical reaction treatment, and excluding N 0 X components such as ammonia from the solid waste. The compression-formed granular intermediate product has a temperature of 50 or more due to heating and the exothermic reaction of Ca0.
これを次の乾燥工程において水分を除き、 かつカルシウムと燃焼 ガス中の炭酸ガスとの反応によって固化し、 取扱い易い固形物がで きる。 これはこのまま燃料として用いることができる。  This is removed in the next drying step, and solidified by the reaction between calcium and carbon dioxide in the combustion gas, so that a solid that can be easily handled is obtained. This can be used as fuel as it is.
日本の都市ごみの実施例では、 キログラム当りの低位発熱量が 4 0 0 0 k ca l 近く になり、 ョ一ロッパの実施例では 3 5 0 0 k ca l になり、 いずれにしても石炭ボイラーによって混焼するのに最適な 物理 · 化学的性状と生物学的に安定した貯留特性を持つ燃料となる c 次に、 上述した廃棄物 Gを廃棄物受入れ槽 1に投入してから乾燥 中和反応器 1 9までの処理工程を経て固形物 Sが得られるが、 前記 廃棄物受入れ槽 1 , 第 1破砕機 3 , 第 2破砕機 7および混合貯留反 応器 1 3に添加する C a 0の全添加量は、 次の手段で決定するのが 好ま しいものである。 In the example of municipal solid waste in Japan, the lower calorific value per kilogram is close to 400 kcal, and in the example of Europe it is 350 kcal, and in any case, the coal boiler It becomes a fuel with optimal physical and chemical properties and biologically stable storage characteristics for co-firing c. Next, the above-mentioned waste G is put into the waste receiving tank 1 and then dried and neutralized Solids S are obtained through the processing steps up to the reactor 19, but the C a 0 added to the waste receiving tank 1, the first crusher 3, the second crusher 7, and the mixed storage reactor 13 is obtained. The total amount is preferably determined by the following means.
すなわち、 都市ごみなどの廃棄物 Gを 1 0 0 %とし、 この廃棄物 G中には、 分析すると、 水分, プラスチック, 無機物および資源化 物が含有されている。 そして、 水分を乾燥機などを使用して W %、 プラスチッ ク, 無機物および資源化物をそれぞれ通常の分析法であ る目視手選分析で P, M, R%を脷定することによって、 有機物 U. %は、 U = 1 0 0— (W + P + M + R ) に基づいて算出される。 That is, the waste G such as municipal solid waste is set at 100%, and when analyzed, this waste G contains moisture, plastics, inorganic substances, and resources. Then, the moisture is reduced to W% using a dryer, etc. By determining P, M, and R% of plastics, inorganic substances, and recyclables by visual selection analysis, which is a common analytical method, the organic matter U.% can be calculated as U = 100— (W + P + M + R).
C a 0の添加量 Aは、 A = K x U (但し、 K : 定数) となり、 し かも、 Kは P , Wの関数である K = f ( P , W) で表されると共に、 C a Oの添加率を決定する補正項であって、 プラスチッ クの混入率 ( P ) と水分率 (W) の比率によって決定されるものである。 原理 的にはプラスチッ クなどに含まれるごみ中の塩素に対して、 燃焼過 程でこれを中和するに必要な C a Oの添加量を算出することによつ て補正する項である。  The added amount A of C a 0 is A = K x U (where K is a constant), and K is represented by K = f (P, W) which is a function of P and W, and C a Correction term for determining the O addition rate, which is determined by the ratio of the plastic mixing rate (P) to the water content (W). In principle, this is a term that is corrected by calculating the amount of CaO required to neutralize chlorine in the garbage contained in plastics, etc. during the combustion process.
本実施例においては世界各国のごみ質に対して適応性を調査した 結果、 K - 0. 2〜 1. 2の範囲で最適な添加率を決定する方法を 規定するものである。  In this example, the method of determining the optimal addition rate in the range of K-0.2 to 1.2 as a result of investigating the adaptability to waste quality in various countries around the world is specified.
Wの項は水分が過剰である場合に、 有機質に対する C a Oの有効 添加率を補正するものである。  The W term corrects for the effective addition of C a O to organic matter when moisture is excessive.
この C a 0の添加率 A%を基にすると、 廃棄物受入れ槽 1 または 第 1破砕機 3では 1〜 2 %を、 第 2破砕機 7では 2 %程度、 混台貯 留反応器 1 3では 1〜 5 %の C a 0を添加して物理♦ 化学反応処理 するのが望ま しいものである。 このように、 廃棄物 Gを処理する各 処理工程で C a 0を添加して物理的および化学的に処理することに より、 生物学的に安定した固形物 S としての燃料または土木建築資 材用素材を得ることができる。  Based on the addition rate A% of C a 0, the waste receiving tank 1 or the first crusher 3 is about 1 to 2%, the second crusher 7 is about 2%, and the mixed-bed storage reactor 13 Then, it is desirable to add 1 to 5% C a 0 and to perform physical and chemical reaction treatment. In this way, by adding C a0 and physically and chemically treating in each treatment step of treating waste G, fuel or civil engineering material as a biologically stable solid S is obtained. Material can be obtained.
なお、 上記の実施例ではアル力リ土類金属酸化物として C a 0を 列にとって説明した力《、 この C a 0に M g 0を混入したものでもよ く 、 また M g 0だけであっても、 さ らに C a (O H) 2 またはその 混台物を用いてもよい。 In the above embodiment, the force described using Ca 0 as a column of the alkaline earth metal oxide << The force obtained by mixing Mg 0 into Ca 0 may be used, or only Mg 0 may be used. Alternatively, C a (OH) 2 or a mixture thereof may be used.
次に、 前述した製造方法によって得られた廃棄物による固形物燃 料 S と、 主と して石炭を使用する天然燃料 Nとの混合によってハイ プリ ッ ド燃料が得られる製造方法を第 2図を用いて説明する。 第 2 図において、 廃棄物による固形物燃料 S.は粉砕機 2 3に投入されて、 この粉砕機 2 3にてさらに細かい粒度に破碎される。 この粉砕機 2 3で破砕された細かな粒状の固形物燃料は比重差分離機 2 5に投入 され、 この比重差分離機 2 5でガラス, 鉄くずなどの不純物 (不燃 物) がさらに餘去される。 Next, Fig. 2 shows a production method in which a hybrid fuel is obtained by mixing solid fuel S from waste obtained by the above-mentioned production method and natural fuel N, which mainly uses coal. This will be described with reference to FIG. No. 2 In the figure, solid fuel S. from waste is put into a crusher 23 and crushed to a finer particle size by the crusher 23. The fine-grained solid fuel crushed by the crusher 23 is fed into a specific gravity separator 25, which further removes impurities (incombustibles) such as glass and iron scraps. Is done.
前記比重差分離機 2 5で不純物が除去された粒状の固形物燃料は 混合器 2 7に投入されると共に、 この混合器 2 7に主として石炭で ある天然燃料 Nが投入される。 したがって、 この混合器 2 7におい ては、 粒状の固形物燃料と天然燃料 Nとが一定の割合で一定時間混 合処理される。  The granular solid fuel from which impurities have been removed by the specific gravity difference separator 25 is charged into the mixer 27, and the natural fuel N, which is mainly coal, is charged into the mixer 27. Therefore, in the mixer 27, the particulate solid fuel and the natural fuel N are mixed at a fixed rate for a fixed time.
前記混合器 2 7で混合処理された混合物は、 例えば圧縮成型機 2 に投入されて圧縮成型され、 さらに乾燥器 3 1で一定の条件下で 乾燥処理が行なわれることによって例えば豆炭や練炭程度の大きさ からなる固形物のハィブリ ッ ド燃料 H A が得られることになる。 The mixture subjected to the mixing treatment in the mixer 27 is, for example, charged into a compression molding machine 2 and compression-molded, and further subjected to a drying treatment under a certain condition in a dryer 31 to thereby obtain, for example, a charcoal or briquette. Haiburi head fuel H a solid consisting of size will be obtained.
前記混合器 2 7で混合処理された混合物は、 場合によっては造粒 機 3 3に投入される。 この造粒機 3 3には水または C a ( O H ) 2 が添加されて一定条件下で造粒される。 さらに乾燥器 3 5で一定条 件下で乾燥処理されることによって、 廃棄物による固形物燃料 Sを 芯にして外周部に天然燃料 Nの層が付着し例えば大豆程度の大きさ からなる粒状の造粒物ハイブリ ッ ド燃料 H B が得られることとなる。 The mixture subjected to the mixing treatment in the mixer 27 is charged into a granulator 33 in some cases. Water or C a (OH) 2 is added to the granulator 33 and granulated under certain conditions. Further, by drying under a certain condition in the dryer 35, a layer of natural fuel N adheres to the outer periphery with the solid fuel S as waste as a core, and a granular material having a size of, for example, soybean is obtained. the fact that the granules hybrid fuel H B is obtained.
このようにして得られた固形物ハイプリ ッ ド燃料 H A や造粒物ハ ィブリ ッ K H B は、 廃棄物による固形物燃料 Sが一定の割合で含有 されているから、 従来の 1 0 0 %の天然燃料 Nのコス トに比べて安 価に製造することができると共に、 天然燃料 N中に含まれている硫 黄や塩素の燃焼によつて生ずる酸性ガスは廃棄物による固形物燃料 Sに含有している C a 0との反応で吸収される。 The solid hybrid fuel H A and the granulated hybrid KH B obtained in this way contain a certain percentage of solid fuel S from waste, so the conventional 100% It can be manufactured at lower cost than the cost of natural fuel N, and the acid gas generated by the combustion of sulfur and chlorine contained in natural fuel N is converted to solid fuel S from waste. It is absorbed by the reaction with the contained C a 0.
このように、 廃棄物による固形物燃料 Sが一定の割合で含有され ていると共に、 固形物燃料 Sには C a 0が含まれていることにより、 排ガスのク リ一ニングが行なわれて環境汚染のないク リーンな燃料 となる。 As described above, the solid fuel S from waste is contained at a certain ratio, and the solid fuel S contains Ca0, so that the exhaust gas is cleaned and the environment is reduced. Clean fuel without pollution Becomes
このハイプリ ッ ド燃料は、 例えば簡易型ス トーブなどの小型ボイ ラー用の燃料と して使用可能であると共に、 品位としては無煙炭に 近く なり、 さらに廃棄物による固形物燃料 Sを含有しているから繊 維質となり、 バイ ンダーと しての効果があり、 造粒し易く なる。 力 口 リーと しては天然燃料 Νと廃棄物による固形物燃料 Sの中間の低 品位石炭並のカロリーを有し、 燃料と して充分使用可能であり、 種 々な燃料の多く の用途に使用できるものである。  This hybrid fuel can be used as fuel for small boilers such as simple stoves, etc., and its quality is close to that of anthracite, and it also contains solid fuel S as waste. From this, it becomes a fiber, has an effect as a binder, and is easily granulated. It has a calorie equivalent to that of low-grade coal, which is intermediate between natural fuel Ν and solid fuel S made from waste, and is sufficiently usable as a fuel, and is suitable for many uses of various fuels. It can be used.
上述した廃棄物 Gを廃棄物受入れ槽 1へ投入してから乾燥中和反 応器 1 9までの処理工程で得られる中間生成物を第 1図に示した焼 却炉 3 7に投入して焼却することができる。  The above-mentioned waste G is put into the waste receiving tank 1, and the intermediate products obtained in the processing steps up to the dry neutralization reactor 19 are put into the incinerator 37 shown in Fig. 1. Can be incinerated.
また、 廃棄物 Gを廃棄物受入れ槽 1 に必要な量だけ投入すると共 に、 その必要な量に応じ、 かつ廃棄物 Gの特性に応じて C a 0を適 宜な添加量だけ添加して物理 · 化学反応処理を行なつた後に、 第 1 破砕機 3に投入することなく 、 点線で示したごとく、 直接焼却炉 3 7に投入して焼却処理しても廃棄物受入れ槽 1でのごみの腐敗化を' 防止すると共に、 燃焼過程での酸性ガスの吸収を効果的に行わせる ことが可能である。  In addition, the required amount of waste G is put into the waste receiving tank 1, and the Ca 0 is added in an appropriate amount according to the required amount and the characteristics of the waste G. After performing the physical and chemical reaction treatments, as shown by the dotted line, without entering the first crusher 3, the refuse in the waste receiving tank 1 can be directly injected into the incinerator 37 even if incinerated. It is possible to prevent the decay of the gas and to effectively absorb the acid gas in the combustion process.
さらに、 前記第 1破砕機 3にて C a 0を適宜な量だけ投入して物 理 ·化学反応処理を行ない、 第 1廃棄物 G 1を、 第 1選別機 5へ流 すことなく、 点線で示したごとく、 直接焼却炉 3 7に投入して焼却 処理しても高効率なク リーンな燃焼を行なう ことができる。  Further, physical and chemical reaction treatment is performed by charging Ca 0 in an appropriate amount in the first crusher 3 and the first waste G 1 is not flown to the first sorter 5 and is indicated by a dotted line. As shown in, high efficiency and clean combustion can be performed even if it is put into the direct incinerator 37 and incinerated.
また前記第 2破砕機 7にて C a 0を適宜な量だけ投入して、 物理 • 化学反応処理を行ない、 第 3廃棄物 G 3を第 2選别機 9へ流すこ となく、 点線で示したごとく、 直接焼却炉 1 3に投入して焼却処理 しても高効率なク リーンな燃焼を行なう ことができる。  Also, in the second crusher 7, a suitable amount of C a0 is charged, a physical / chemical reaction treatment is performed, and the third waste G3 does not flow to the second selector 9, but is indicated by a dotted line. As shown in the figure, high efficiency and clean combustion can be achieved even if the waste is put into the direct incinerator 13 and incinerated.
産業上の利用可能性  Industrial applicability
以上のように、 この発明にかかる廃棄物による固形物の製造方法 によって得られた固形物 Sは、 まず燃料と して有効に活用されると 共に、 燃料費のコス トダウンが図ら lる。 また天然燃料と混合する ことによって、 天然燃料の使用量が減らされる。 また、 この固形As described above, the solid matter S obtained by the method for producing solid matter from waste according to the present invention is considered to be first effectively used as fuel. In both cases, fuel costs are reduced. Blending with natural fuels also reduces the use of natural fuels. Also, this solid
Sの燃料を直接焼却炉 3 7に投入することによってク リーンな燃焼 を行ない、 そのエネルギーの活用が図られる。 さらに、 得られた固 形物 Sは燃料以外に土木建築資材の素材などに有効に利用される。 By injecting the S fuel directly into the incinerator 37, clean combustion is performed and the energy is used. Furthermore, the obtained solids S are effectively used as materials for civil engineering and construction materials in addition to fuel.

Claims

請 求 の 範 囲 The scope of the claims
1. 都市ごみなどの廃棄物を廃棄物受入れ槽 ( 1 ) に投入した後、 铕 1破砕機 ( 3 ) , 第 2破砕機 ( 7 ) , 混合聍留反応器 ( 1 3) を 経て乾燥中和反応器 ( 1 9 ) で乾燥固化して固形物を製造する際に アルカ リ土類金属酸化物の前記廃棄物の特性に応じた添加量を添加 して合理的に物理 ·化学反応処理を行なう ことを特徴とする廃棄物 による固形物の製造方法。  1. After the waste such as municipal waste is put into the waste receiving tank (1), it is being dried through the 铕 1 crusher (3), the second crusher (7), and the mixed distillation reactor (1 3). When the solidified product is manufactured by drying and solidifying in the sum reactor (19), the physical and chemical reaction treatment can be rationally performed by adding an amount of the alkaline earth metal oxide according to the characteristics of the waste. A method for producing solid matter from waste, characterized in that it is performed.
2. 前記廃棄物受入れ槽 ( 1 ) または第 1破砕機 ( 3) において、 前記廃棄物に対してアル力 リ土類金属酸化物の全添加量の 0〜 3 0 %を添加して物理 · 化学反応処理することを特徴とする請求項 1記 載の廃棄物による固形物の製造方法。  2. In the waste receiving tank (1) or the first crusher (3), 0 to 30% of the total amount of alkaline earth metal oxide is added to the waste, and The method for producing a solid from waste according to claim 1, wherein the solid is subjected to a chemical reaction treatment.
3. 前記第 2破砕機 ( 7 ) において、 前記廃棄物に対してアルカ リ 土類金属酸化物の全添加量の 0〜 5 0 %を添加して物理 · 化学反応 処理することを特徴とする請求項 1記載の廃棄物による固形物の製 造方法。  3. In the second crusher (7), a physical-chemical reaction treatment is performed by adding 0 to 50% of the total amount of the alkaline earth metal oxide to the waste. A method for producing a solid matter from the waste according to claim 1.
4. 前記混合貯留反応器 ( 1 3 ) において前記廃棄物に対してアル 力 リ土類金属酸化物の全添加量の 20〜 1 0 0 %を添加して物理 · 化学反応処理を行なうことを特徴とする請求項 1記載の廃棄物によ る固形物の製造方法。  4. In the mixed storage reactor (13), a physical and chemical reaction treatment is performed by adding 20 to 100% of the total amount of alkaline earth metal oxide to the waste. A method for producing a solid matter from waste according to claim 1.
5. 前記廃棄物受入れ槽 ( 1 ) , 第 1破砕機 ( 3) , 第 2破砕機 ( 7 ) および混合貯留反応器 ( 1 3 ) の複数箇所においてアル力リ 土類金属酸化物の全添加量を適宜な比率で添加して物理化学的反応 処理することを特徴とする請求項 1記載の廃棄物による固形物の製 造方法。  5. Total addition of earth metal oxides at multiple locations of the waste receiving tank (1), the first crusher (3), the second crusher (7) and the mixed storage reactor (13) 2. The method for producing a solid substance from waste according to claim 1, wherein the physicochemical reaction treatment is performed by adding an appropriate amount of the solid substance.
6. 廃棄物にアル力リ土類金属酸化物を添加して固形物を製造する に際して、 前記廃棄物を構成する水分 W%, プラスチッ ク P %, 無 機物 M%および資源化物 R%を分析測定して、 11 = 1 0 0 - (W + P +M + R) に基づき有機物 U%を算出すると共に、 アルカリ土類 金厲酸化物の最適な添加量 Aを、 A = K X U [但し、 K = f ( P , 2/01771 PCT/JP91/00961 6. When solid waste is produced by adding alkaline earth metal oxide to waste, water W%, plastic P%, inorganic matter M%, and resources R% that constitute the waste are removed. Analytically measure and calculate the organic matter U% based on 11 = 100-(W + P + M + R), and determine the optimal amount A of alkaline earth gold oxide as A = KXU [ , K = f (P, 2/01771 PCT / JP91 / 00961
20 ~ -  20 ~-
W) ] を基にし決定して廃棄物にアルカリ土類金属酸化物を添加す ることを特徴とする廃棄物による固形物の製造方法。 W)], and adding an alkaline earth metal oxide to the waste.
7. 前記 Kの値を 0. 0 2〜 0. 1 2の範囲とすることを特徵とす る請求項 6記載の廃棄物による固形物の製造方法。  7. The method according to claim 6, wherein the value of K is in the range of 0.02 to 0.12.
8. 予め細破砕された廃棄物と適宜な量のアル力リ土類金属酸化物 を含んだ添加材を混合貯留反応器 ( 1 3 ) に投入して混合 ·反応を 行なった後、 反応された第 1生成廃棄物を混合脱気反応器 ( 1 5 ) に投入し、 適宜な量のアル力 リ土類金属酸化物を含んだ添加材を必 要に応じて添加し、 混合反応および反応生成ガスの脱気を行ない、 反応された第 2生成廃棄物を圧縮成型器 ( 1 7) に投入して圧縮成 型を行ない、 次いで、 圧縮成型された第 3生成廃棄物を乾燥中和反 応器 ( 1 9 ) に投入して乾燥中和反応を行ない、 さらに必要に応じ て篩分器にて篩分して固形物を得ることを特徴とする廃棄物による 固形物の製造方法。  8. The pre-crushed waste and an appropriate amount of additive containing alkaline earth metal oxide are put into the mixing and storage reactor (13), mixed and reacted, and then reacted. Into the mixed degassing reactor (15), add an appropriate amount of additive containing alkaline earth metal oxide as necessary, and mix and react. The produced gas is degassed, the reacted second product waste is put into a compression molding machine (17) to perform compression molding, and then the compression molded third product waste is dried and neutralized. A method for producing solids from waste, characterized in that the solids are introduced into a reactor and subjected to a dry neutralization reaction, and, if necessary, sieved with a sieve to obtain solids.
9. 前記混合貯留反応器 ( 1 3 ) における反応を密閉状態下、 温度 60 以上 1 0 ◦て以下で 1時間以上行ない、 混合脱気反応器 ( 1 5 ) における反応を排気状態下、 前記温度より少なく とも 5 以上 高い温度で 5分間以上行なう ことを特徴とする請求項 8記載の廃棄 物による固形物の製造方法。  9. The reaction in the mixed storage reactor (13) is carried out in a closed state at a temperature of 60 to 10 ° for 1 hour or more, and the reaction in the mixed degassing reactor (15) is exhausted. 9. The method for producing solids from waste according to claim 8, wherein the method is performed at least 5 minutes or more at a high temperature.
1 0. 予め細破砕された廃棄物とするために、 廃棄物を第 1破砕機 ( 3) で粗破砕すると共に不燃物を選別除去し、 次いで破砕された 廃棄物に適宜な量のアル力リ土類金属酸化物を含んだ添加材を投入 し、 第 2破砕機 (7 ) で破砕すると共に不燃物を選別除去し、 必要 に応じて第 3破碎機 ( 1 1 ) で破砕して細破砕された廃棄物とする ことを特徵とする請求項 8記載の廃棄物による固形物の製造方法。 10 0. In order to make the waste finely crushed in advance, the waste is roughly crushed by the first crusher (3), and the non-combustible material is selectively removed. Then, an appropriate amount of force is applied to the crushed waste. An additive containing an earth metal oxide is introduced, crushed by a second crusher (7), and non-combustible materials are removed by screening. If necessary, crushed by a third crusher (11) 9. The method for producing solids from waste according to claim 8, wherein the waste is crushed waste.
1 1. 前記反応された第 1生成廃棄物、 前記脱気反応された第 2生 成廃棄物、 あるいは前記篩分器 ( 2 1 ) にて篩分された粉体の廃棄 物を必要に応じてかつ、 必要な量だけ前記混合貯留反応器 ( 1 3 ) に還流することを特徵とする請求項 8記載の廃棄物による固形物の 製造方法。 1 1. The reacted first product waste, the degassed second product waste, or the powder waste sieved by the sieving device (21) as required 9. The method according to claim 8, wherein a required amount of the mixture is refluxed to the mixed storage reactor (13). Production method.
1 2. 廃棄物による固形物 ( S ) に、 天然燃料 (N) を混合した後、 圧縮成型加工あるいは造拉加工を行なって、 ハイプリ ッ ド燃料を得 ることを特徴とする廃棄物による固形物の製造方法。  1 2. Solid fuel solid waste (S) is mixed with natural fuel (N) and then subjected to compression molding or kidnapping to obtain hybrid fuel. Method of manufacturing a product.
1 3. 都市ごみなどの廃棄物を廃棄物受入れ槽 ( 1 ) に投入した後 に焼却炉 ( 3 7 ) に投入して廃棄物を焼却する際、 前記廃棄物受入 れ槽 ( 1 ) にアルカ リ土類金属酸化物の前記廃棄物の特性に応じた 添加量を添加して合理的な物理 ·化学反応処理を行なう ことを特徴 とする廃棄物の焼却方法。  1 3. When waste such as municipal solid waste is put into the waste receiving tank (1) and then put into the incinerator (37) for incineration of waste, the waste receiving tank (1) is placed in the waste receiving tank (1). A waste incineration method, characterized in that a rational addition of an amount of an earth metal oxide according to the characteristics of the waste is performed to perform a rational physical / chemical reaction treatment.
1 4. 都市ごみなどの廃棄物を廃棄物受入れ槽 ( 1 ) に投入した後、 第 1破砕機 ( 3 ) を経て焼却炉 ( 3 7 ) に投入して廃棄物を焼却す る際、 前記廃棄物受入れ槽 ( 1 ) および第 1破砕機 ( 3 ) の両方ま たはいずれか一方にアル力リ土類金属酸化物の前記廃棄物の特性に 応じた添加量を添加して合理的に物理 ·化学反応処理を行なう こと を特徴とする廃棄物の焼却方法。  1 4. After injecting waste such as municipal solid waste into the waste receiving tank (1), pass it through the first crusher (3) to the incinerator (37) to incinerate the waste. The waste receiving tank (1) and / or the first crusher (3) are added in an amount corresponding to the characteristics of the waste of the alkaline earth metal oxide to a reasonable ratio. A waste incineration method characterized by performing physical and chemical reaction treatments.
1 5. 都市ごみなどの廃棄物を廃棄物受入れ槽 ( 1 ) に投入した後、 第 1破砕機 ( 3) , 第 2選別機 ( 5) および第 2破砕機 ( 7 ) を経 て焼却炉 ( 37 ) に投入して廃棄物を焼却する際、 前記廃棄物受入 .れ槽 ( 1 ) , 第 1破砕機 ( 3 ) および第 2破砕機 ( 7 ) の複数箇所 またはいずれかにアル力リ土類金属酸化物の前記廃棄物の特性に応 じた添加量を添加して合理的に物理 · 化学反応処理を行なうことを 特徴とする廃棄物の焼却方法。  1 5. After the waste such as municipal solid waste is put into the waste receiving tank (1), it goes through the first crusher (3), the second sorter (5) and the second crusher (7), When the waste is put into (37) and incinerated, the waste receiving tank (1), the first crusher (3) and / or the second crusher (7) can be used in several places or in any place. A waste incineration method characterized by adding an amount of an earth metal oxide according to the properties of the waste to perform a physicochemical reaction rationally.
1 6. 都市ごみなどの廃棄物を廃棄物受入れ槽 ( 1 ) に投入した後、 第 1破碎機 ( 3) , 第 1選別機 ( 5) , 第 2破砕機 ( 7 ) , 第 2選 別機 ( 9 ) および混合貯留反応器 ( 1 3 ) を経て焼却炉 ( 37 ) に 投入して廃棄物を焼却する際、 前記廃棄物受入れ槽 ( 1 ) 、 第 1破 砕機 ( 3) 、 第 2破砕機 ( 7 ) および混合貯留反応器 ( 1 3 ) の複 数箇所またはいずれかにアル力 リ土類金属酸化物の前記廃棄物の特 性に応じた添加量を添加して合理的に物理 · 化学反応処理を行なう ことを特徵とする廃棄物の焼却方法。 . 1 6. After the waste such as municipal waste is put into the waste receiving tank (1), the first crusher (3), the first sorter (5), the second crusher (7), the second sorter The waste receiving tank (1), the first crusher (3), and the second crusher (3) are put into the incinerator (37) through the crusher (9) and the mixed storage reactor (13) to incinerate the waste. The crusher (7) and / or the mixed storage reactor (13) are added to multiple or any of the mixed storage reactors (13) at an appropriate amount according to the characteristics of the waste of the alkaline earth metal oxide. · Perform chemical reaction processing Waste incineration method. .
PCT/JP1991/000961 1990-07-20 1991-07-19 Method of turning wastes into solid body and method of burning such solid body WO1992001771A1 (en)

Applications Claiming Priority (8)

Application Number Priority Date Filing Date Title
JP2193798A JP2954990B2 (en) 1990-07-20 1990-07-20 Method of manufacturing solid fuel from waste
JP2/193798 1990-07-20
JP2/401438 1990-12-11
JP2401438A JPH04210284A (en) 1990-12-11 1990-12-11 Production of solid from waste refuse
JP3032760A JP2798189B2 (en) 1991-02-27 1991-02-27 How to incinerate waste
JP3/32760 1991-02-27
JP3071221A JP3067827B2 (en) 1991-04-03 1991-04-03 Hybrid fuel manufacturing method
JP3/71221 1991-04-03

Publications (1)

Publication Number Publication Date
WO1992001771A1 true WO1992001771A1 (en) 1992-02-06

Family

ID=27459673

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/JP1991/000961 WO1992001771A1 (en) 1990-07-20 1991-07-19 Method of turning wastes into solid body and method of burning such solid body

Country Status (1)

Country Link
WO (1) WO1992001771A1 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0894846A2 (en) * 1997-07-22 1999-02-03 Mutabor GmbH, Management für Umwelt Technologie, Abfallwirtschaft Beratung Organisation und Verkauf Recycling Finely divided fuel and method of making the same
CN109078965A (en) * 2018-09-17 2018-12-25 东莞理工学院 A kind of Changing Urban Garbage into Resources processing system
CN109385317A (en) * 2018-11-26 2019-02-26 安徽吉露科技有限公司 A kind of preparation method of new energy materials
CN109609235A (en) * 2019-01-02 2019-04-12 镇江市中运城市环境治理有限公司 A kind of production technology of environment-friendly garbage regenerated coal

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5521441A (en) * 1978-08-01 1980-02-15 Dainekorojii Inc Briquet containing caking coal and life waste
JPS55107824A (en) * 1979-02-15 1980-08-19 Kawasaki Steel Corp Reducing method for sox concentration in exhaust-gas from incinerator on burning waste of high sulfur content
JPS60147496A (en) * 1984-01-11 1985-08-03 Fuji Electric Co Ltd Processing of plastic-containing waste into solid fuel and device therefor
JPS60186596A (en) * 1983-12-05 1985-09-24 ヨ−スト エドウアルド マヨ−ル Fuel briquette
JPS6140398A (en) * 1984-07-31 1986-02-26 Toshiro Watanabe Method for treatment utilizing waste as water-repellent solid fuel

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5521441A (en) * 1978-08-01 1980-02-15 Dainekorojii Inc Briquet containing caking coal and life waste
JPS55107824A (en) * 1979-02-15 1980-08-19 Kawasaki Steel Corp Reducing method for sox concentration in exhaust-gas from incinerator on burning waste of high sulfur content
JPS60186596A (en) * 1983-12-05 1985-09-24 ヨ−スト エドウアルド マヨ−ル Fuel briquette
JPS60147496A (en) * 1984-01-11 1985-08-03 Fuji Electric Co Ltd Processing of plastic-containing waste into solid fuel and device therefor
JPS6140398A (en) * 1984-07-31 1986-02-26 Toshiro Watanabe Method for treatment utilizing waste as water-repellent solid fuel

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0894846A2 (en) * 1997-07-22 1999-02-03 Mutabor GmbH, Management für Umwelt Technologie, Abfallwirtschaft Beratung Organisation und Verkauf Recycling Finely divided fuel and method of making the same
EP0894846A3 (en) * 1997-07-22 1999-04-14 Mutabor GmbH, Management für Umwelt Technologie, Abfallwirtschaft Beratung Organisation und Verkauf Recycling Finely divided fuel and method of making the same
CN109078965A (en) * 2018-09-17 2018-12-25 东莞理工学院 A kind of Changing Urban Garbage into Resources processing system
CN109385317A (en) * 2018-11-26 2019-02-26 安徽吉露科技有限公司 A kind of preparation method of new energy materials
CN109609235A (en) * 2019-01-02 2019-04-12 镇江市中运城市环境治理有限公司 A kind of production technology of environment-friendly garbage regenerated coal

Similar Documents

Publication Publication Date Title
EP1370631B1 (en) Conversion of municipal solid waste to high fuel value
US10240091B2 (en) Process for devolatizing a feedstock
CN101758059B (en) Garbage and sludge high pressure themolysis processing method, system and application thereof
CN101693251B (en) Thermal cracking resource processing technology of domestic refuse in marine ships
CN102357516B (en) Linkage process of municipal waste pre-treatment and cement kiln resource comprehensive utilization and system thereof
CN101782235A (en) Harmless incineration disposal system and method for disposing domestic refuges
CN104084414A (en) Recycling method of combustible solid waste
CN102350428B (en) Equipment for producing composite dry powder fuel used for coal-fired power plant generation with municipal domestic waste and industrialization method thereof
CN110976472A (en) Kitchen waste and household waste co-processing method
CN108977251A (en) It is a kind of using house refuse preparation biomass can charcoal system and method
CN107962064A (en) A kind of house refuse produces day clear processing method daily
CN104671715A (en) Method for preparing light-weight protection wall by utilizing flying ash generated after garbage power
CN102658284A (en) Advanced municipal refuse harmless reclamation treatment method
KR102344255B1 (en) Method for manufacturing powder regenerative fuels using petrochemical waste and combustible powder production apparatus thereof
WO1992001771A1 (en) Method of turning wastes into solid body and method of burning such solid body
KR101296043B1 (en) Using waste coal briquet and manufacturing method thereof
CN102441560A (en) Domestic garbage compression-classification-comprehensive disposal-and-utilization system and device
CN107457245A (en) A kind of residents in rural community recycling processing method
JP3122487B2 (en) Manufacturing method of solidified body from municipal solid waste
JP3236331B2 (en) Method for producing solids from waste
JPH05185062A (en) Production of solid material with waste
JPH04210284A (en) Production of solid from waste refuse
JP2798189B2 (en) How to incinerate waste
JP2954990B2 (en) Method of manufacturing solid fuel from waste
CN102827663A (en) Preparation method for jointly processed mineralized refuse derived fuel suitable for cement kiln

Legal Events

Date Code Title Description
AK Designated states

Kind code of ref document: A1

Designated state(s): CA FI KR US

AL Designated countries for regional patents

Kind code of ref document: A1

Designated state(s): AT BE CH DE DK ES FR GB NL SE

NENP Non-entry into the national phase

Ref country code: CA